CN107935102A - A kind of method that water removal moderate resistance life element is removed using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic - Google Patents

A kind of method that water removal moderate resistance life element is removed using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic Download PDF

Info

Publication number
CN107935102A
CN107935102A CN201711245269.6A CN201711245269A CN107935102A CN 107935102 A CN107935102 A CN 107935102A CN 201711245269 A CN201711245269 A CN 201711245269A CN 107935102 A CN107935102 A CN 107935102A
Authority
CN
China
Prior art keywords
magnetic
bismuth oxyiodide
persulfuric acid
acid hydrogen
hydrogen salt
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.)
Pending
Application number
CN201711245269.6A
Other languages
Chinese (zh)
Inventor
张永丽
刘杨
郭洪光
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.)
Sichuan University
Original Assignee
Sichuan University
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 Sichuan University filed Critical Sichuan University
Priority to CN201711245269.6A priority Critical patent/CN107935102A/en
Publication of CN107935102A publication Critical patent/CN107935102A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/84Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/843Arsenic, antimony or bismuth
    • B01J23/8437Bismuth
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/33Electric or magnetic 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
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic properties
    • 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
    • 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
    • C02F2101/34Organic compounds containing oxygen
    • 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
    • C02F2101/36Organic compounds containing halogen
    • 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
    • C02F2101/38Organic compounds containing nitrogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Catalysts (AREA)

Abstract

A kind of method that water removal moderate resistance life element is removed using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic, it is related to a kind of method for removing residual antibiotic in water removal.The invention aims to of high cost, problem the defects of poor removal effect and complex process that solves the existing method for removing water removal moderate resistance life element.Method:First, persulfuric acid hydrogen salt is mixed with the pretreated water containing antibiotic;2nd, pH value in reaction is adjusted;3rd, magnetic bismuth oxyiodide is prepared;4th, add magnetic bismuth oxyiodide and use radiation of visible light mixed solution;5th, magnetic bismuth oxyiodide is separated using external magnetic field, that is, completes a kind of method that water removal moderate resistance life element is removed using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic.The plain efficiency of water removal moderate resistance life is gone to reach 75%~95% using the method for the present invention.The present invention can go residues of antibiotics in water removal.

Description

One kind goes water removal moderate resistance using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic The method of raw element
Technical field
The present invention relates to a kind of method for removing water removal moderate resistance life element.
Background technology
With the quickening of social process of industrialization, the compound with antibiotic effect is added as detergent, lubricating oil The fields such as the main component of agent, plasticizer etc. is widely used in weaving, cleans, pesticidal emulsifiable, and hospital wastewater, sewage treatment plant And the random discharge of plant effuent etc., cause environment antibiotic content in natural water to increase year by year, to the safe structure of ambient water quality Into very big threat.
At present both at home and abroad remove water environment in the common method of antibiotic include bioanalysis, physico-chemical process, electrochemical process and Membrane-filter procedure.Since antibiotic is to the toxic action of biology so that effect ten is removed to it without special acclimated microorganism Divide limited;Electrochemical process is due to higher to low concentration pollutant processed in units cost, it is difficult to large-scale use;Though membrane technology is wide It is general to be applied to environment water process, however higher membrane module equipment and operating cost make its be difficult to remove on a large scale it is specific organic Play a role in pollutant;Photocatalytic oxidation in physico-chemical process due to reaction rate is fast, removal efficiency is high, cost is controllable and It is widely applied in water process, but catalyst existing for this method is difficult to recycle, regeneration cost and energy consumption are excessive asks Topic, makes it still have certain limitation in application study.
The content of the invention
The invention aims to solve the problems, such as existing to go that feature antibiotic is difficult in water removal, treatment effeciency is low, there is provided A kind of method that water removal moderate resistance life element is removed using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic.
A kind of method that water removal moderate resistance life element is removed using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic, is specifically Complete according to the following steps:
First, persulfuric acid hydrogen salt is mixed with the pretreated water containing antibiotic, then with mixing speed is at room temperature 160 r/min The min of 20 min ~ 45 is stirred under conditions of ~ 250 r/min, obtains the mixed solution of persulfuric acid hydrogen salt and pretreated water;
Persulfuric acid hydrogen salt described in step 1 is in potassium hydrogen persulfate, hydrogen persulfate ammonium, hydrogen persulfate sodium and hydrogen persulfate calcium One kind or wherein several mixtures;
The concentration of antibiotic is 0.01~100 mg/L in pretreated water described in step 1:
The mass ratio of the quality of persulfuric acid hydrogen salt described in step 1 and the water of pretreatment is 1:(1000~10000);
2nd, adjust pH value in reaction, low whipping speed under conditions of the r/min of 150 r/min~200 using 0.1 mol/L ~ The perchloric acid of 100 mol/L and the sodium hydroxide solution of 0.1mol/L ~ 100mol/L are by persulfuric acid hydrogen salt and pretreated water The pH values of mixed solution are adjusted to 6.5 ~ 7.5, the mixed solution of persulfuric acid hydrogen salt and pretreated water after adjusted pH values;
3rd, magnetic bismuth oxyiodide is prepared:
1., by Fe3O4Mass fraction is added to as in 97% ~ 99% ethylene glycol, vigorous magnetic stirs 10 min, reuses ultrasonic wave Scattered 30 min of concussion instrument concussion, obtain Fe3O4With the mixed solution of ethylene glycol;
Step 3 1. described in Fe3O4Quality and the volume ratio of ethylene glycol solution that mass fraction is 97% ~ 99% be (0.001g~10g):1 mL;
2., the mixed solution of bismuth nitrate and absolute ethyl alcohol, potassium iodide aqueous solution be added sequentially to Fe3O4With the mixing of ethylene glycol In solution, after magnetic agitation 60min, mixing suspension is obtained;
Step 3 2. described in bismuth nitrate and absolute ethyl alcohol mixed solution in the concentration of bismuth nitrate be 0.01 ~ 10 mol/L;
Step 3 2. described in bismuth nitrate and absolute ethyl alcohol mixed solution and Fe3O4With the volume of the mixed solution of ethylene glycol Than for (0.1 ~ 100):1;
Step 3 2. described in potassium iodide aqueous solution in the concentration of potassium iodide be 0.01 ~ 10 mol/L;
Step 3 2. described in potassium iodide aqueous solution and Fe3O4Volume ratio with the mixed solution of ethylene glycol is (0.1 ~ 100): 1;
3., will using the sodium hydroxide solution of the mol/L of the perchloric acid of the mol/L of 0.1 mol/L ~ 100 and 0.1 mol/L ~ 100 Mixing suspension is adjusted to certain ph, then mixing suspension is added to the stainless steel reaction under high pressure that liner is polytetrafluoroethylene (PTFE) In kettle, then stainless steel autoclave sealed, the stainless steel autoclave after sealing is reacted at 120 DEG C ~ 200 DEG C 12h ~ 48h, obtains magnetic bismuth oxyiodide suspension;
Step 3. described in mixing suspension certain ph be pH 1.0 ~ 7.0;
4., by step 3. in obtained magnetic bismuth oxyiodide suspension in centrifugal speed under the r/min of 6500 r/min ~ 8000 The min of 10 min ~ 30, the deposit after being centrifuged is centrifuged;Deionized water and washes of absolute alcohol is respectively adopted Deposit after centrifugation each 5 times ~ 10 times, then dry 6h ~ 24h in the case where temperature is -18 DEG C ~ 80 DEG C, obtain Tan solid As magnetic bismuth oxyiodide;
4th, add magnetic bismuth oxyiodide and use radiation of visible light mixed solution;
In persulfuric acid hydrogen salt and the mixed solution of pretreated water that magnetic bismuth oxyiodide is added to after adjusting pH values, reuse Visible light source irradiates mixed solution, and the min of 10 min of reaction time ~ 240, obtains the water containing the bismuth oxyiodide that is magnetic;
The dosage of magnetic bismuth oxyiodide described in step 4 is the mg/L of 1 mg/L ~ 200;
Visible light source power described in step 4 is the W of 10 W ~ 1000;
5th, magnetic bismuth oxyiodide is separated using external magnetic field:The water containing the bismuth oxyiodide that is magnetic is separated using external magnetic field, is returned Magnetic BiOX is received, the glass fibre membrane that aperture is 0.45 μm is reused and the magnetic bismuth oxyiodide of recycling is filtered, then Cleaned 5 times ~ 10 times using deionized water and absolute ethyl alcohol are each to the magnetic bismuth oxyiodide difference after filtering respectively, then be in temperature 12h ~ 48h is dried in vacuo at 50 DEG C ~ 75 DEG C, the magnetic bismuth oxyiodide after being regenerated and the water for removing water removal moderate resistance life element.
The principle of the present invention:
intermediateproducts
In the present invention on photochemical catalyst bismuth oxyiodide surface under visible light illumination, positioned at the photoelectron transition of forbidden band, formed empty Cave electronics pair(h+-eCB -).HSO in reaction system in the photoelectron and potassium hydrogen persulfate on bismuth oxyiodide surface5 -Or SO5 2-Occur Electronics shifts, so that persulfuric acid hydrogen radical is cracked into SO4 -With OH-;In addition, rest on photochemical catalyst bismuth oxyiodide surface Hole, can be by HSO5 -Activation generation SO5 -Free radical, accelerates the removal rate of antibiotic;On the other hand it is supported on iodine The Fe on bismuth oxide surfaceHSO can be activated5 -So that the SO in reaction system4 -With OH-Quantity further increases, so as to accelerate The oxidative degradation of antibiotic.
Embodiment
Embodiment one:Present embodiment is that one kind utilizes persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic The method of water removal moderate resistance life element is gone to complete according to the following steps:
First, persulfuric acid hydrogen salt is mixed with the pretreated water containing antibiotic, then with mixing speed is at room temperature 160 r/min The min of 20 min ~ 45 is stirred under conditions of ~ 250 r/min, obtains the mixed solution of persulfuric acid hydrogen salt and pretreated water;
Persulfuric acid hydrogen salt described in step 1 is in potassium hydrogen persulfate, hydrogen persulfate ammonium, hydrogen persulfate sodium and hydrogen persulfate calcium One kind or wherein several mixtures;
The concentration of antibiotic is 0.01~100 mg/L in pretreated water described in step 1:
The mass ratio of the quality of persulfuric acid hydrogen salt described in step 1 and the water of pretreatment is 1:(1000~10000);
2nd, adjust pH value in reaction, low whipping speed under conditions of the r/min of 150 r/min~200 using 0.1 mol/L ~ The perchloric acid of 100 mol/L and the sodium hydroxide solution of 0.1mol/L ~ 100mol/L are by persulfuric acid hydrogen salt and pretreated water The pH values of mixed solution are adjusted to 6.5 ~ 7.5, the mixed solution of persulfuric acid hydrogen salt and pretreated water after adjusted pH values;
3rd, magnetic bismuth oxyiodide is prepared:
1., by Fe3O4Mass fraction is added to as in 97% ~ 99% ethylene glycol, vigorous magnetic stirs 10 min, reuses ultrasonic wave Scattered 30 min of concussion instrument concussion, obtain Fe3O4With the mixed solution of ethylene glycol;
Step 3 1. described in Fe3O4Quality and the volume ratio of ethylene glycol solution that mass fraction is 97% ~ 99% be (0.001g~10g):1 mL;
2., the mixed solution of bismuth nitrate and absolute ethyl alcohol, potassium iodide aqueous solution be added sequentially to Fe3O4With the mixing of ethylene glycol In solution, after magnetic agitation 60min, mixing suspension is obtained;
Step 3 2. described in bismuth nitrate and absolute ethyl alcohol mixed solution in the concentration of bismuth nitrate be 0.01 ~ 10 mol/L;
Step 3 2. described in bismuth nitrate and absolute ethyl alcohol mixed solution and Fe3O4With the volume of the mixed solution of ethylene glycol Than for (0.1 ~ 100):1;
Step 3 2. described in potassium iodide aqueous solution in the concentration of potassium iodide be 0.01 ~ 10 mol/L;
Step 3 2. described in potassium iodide aqueous solution and Fe3O4Volume ratio with the mixed solution of ethylene glycol is (0.1 ~ 100): 1;
3., will using the sodium hydroxide solution of the mol/L of the perchloric acid of the mol/L of 0.1 mol/L ~ 100 and 0.1 mol/L ~ 100 Mixing suspension is adjusted to certain ph, then mixing suspension is added to the stainless steel reaction under high pressure that liner is polytetrafluoroethylene (PTFE) In kettle, then stainless steel autoclave sealed, the stainless steel autoclave after sealing is reacted at 120 DEG C ~ 200 DEG C 12h ~ 48h, obtains magnetic bismuth oxyiodide suspension;
Step 3. described in mixing suspension certain ph be pH 1.0 ~ 7.0;
4., by step 3. in obtained magnetic bismuth oxyiodide suspension in centrifugal speed under the r/min of 6500 r/min ~ 8000 The min of 10 min ~ 30, the deposit after being centrifuged is centrifuged;Deionized water and washes of absolute alcohol is respectively adopted Deposit after centrifugation each 5 times ~ 10 times, then dry 6h ~ 24h in the case where temperature is -18 DEG C ~ 80 DEG C, obtain Tan solid As magnetic bismuth oxyiodide;
4th, add magnetic bismuth oxyiodide and use radiation of visible light mixed solution;
In persulfuric acid hydrogen salt and the mixed solution of pretreated water that magnetic bismuth oxyiodide is added to after adjusting pH values, reuse Visible light source irradiates mixed solution, and the min of 10 min of reaction time ~ 240, obtains the water containing the bismuth oxyiodide that is magnetic;
The dosage of magnetic bismuth oxyiodide described in step 4 is the mg/L of 1 mg/L ~ 200;
Visible light source power described in step 4 is the W of 10W ~ 1000;
5th, magnetic bismuth oxyiodide is separated using external magnetic field:The water containing the bismuth oxyiodide that is magnetic is separated using external magnetic field, is returned Magnetic BiOX is received, the glass fibre membrane that aperture is 0.45 μm is reused and the magnetic bismuth oxyiodide of recycling is filtered, then Cleaned 5 times ~ 10 times using deionized water and absolute ethyl alcohol are each to the magnetic bismuth oxyiodide difference after filtering respectively, then be in temperature 12h ~ 48h is dried in vacuo at 50 DEG C ~ 75 DEG C, the magnetic bismuth oxyiodide after being regenerated and the water for removing water removal moderate resistance life element.
The principle of present embodiment:
intermediateproducts
In present embodiment on photochemical catalyst bismuth oxyiodide surface under visible light illumination, positioned at the photoelectron transition of forbidden band, shape Into hole-electron pair(h+-eCB -).HSO in reaction system in the photoelectron and potassium hydrogen persulfate on bismuth oxyiodide surface5 -Or SO5 2- Generation electronics shifts, so that persulfuric acid hydrogen radical is cracked into SO4 -With OH-;In addition, rest on photochemical catalyst bismuth oxyiodide The hole on surface, can be by HSO5 -Activation generation SO5 -Free radical, accelerates the removal rate of antibiotic;On the other hand load Fe on bismuth oxyiodide surfaceHSO can be activated5 -So that the SO in reaction system4 -With OH-Quantity further increases, so that Accelerate the oxidative degradation of antibiotic.
The advantages of present embodiment:
First, present embodiment is easy to operate, and degradation by-products are nontoxic;
2nd, present embodiment is to be reacted at normal temperatures and pressures, saves the energy, the method that the antibiotic in water removal is removed with other Compare, reduce cost 45% ~ 70%;
3rd, the magnetic bismuth oxyiodide synthesized by present embodiment can be easier to recycle and regenerate;
4th, present embodiment has good removal rate to antibiotic in water, and up to 80%~95%.
Embodiment two:Present embodiment is with one difference of embodiment:Pre- place described in step 1 It is the one or more in lavo-ofloxacin, Ciprofloxacin, Norfloxacin, gatifloxacin and fleraxacin to manage the antibiotic in water Mixture, other steps are identical with embodiment one.
Embodiment three:Present embodiment is with one of embodiment one or two difference:Institute in step 1 The mass ratio of the quality for the persulfuric acid hydrogen salt stated and the water of pretreatment is 1:(1000 ~ 5000), other steps and specific embodiment party Formula one or two is identical.
Embodiment four:Present embodiment is with one of embodiment one to three difference:Institute in step 1 The mass ratio of the quality for the persulfuric acid hydrogen salt stated and the water of pretreatment is 1:(5000 ~ 8000), other steps and specific embodiment party Formula one to three is identical.
Embodiment five:Present embodiment is with one of embodiment one to four difference:Step 3 1. in The power of the ultrasonic oscillation instrument is the W of 100 W ~ 1000, other steps are identical with embodiment one to four.
Embodiment six:Present embodiment is with one of embodiment one to five difference:1. step 3 is planted The Fe3O4Particle diameter be the nm of 15 nm ~ 500, other steps are identical with embodiment one to five.
Embodiment seven:Present embodiment is with one of embodiment one to six difference:1. step 3 is planted The Fe3O4Particle diameter be the nm of 500 nm ~ 2000, other steps are identical with embodiment one to six.
Embodiment eight:Present embodiment is with specific implementation one of embodiment one to seven difference:Step 4 Described in the dosage of magnetic bismuth oxyiodide be the mg/L of 1 mg/L ~ 10, other steps and the phase of embodiment one to seven Together.
Embodiment nine:Present embodiment is with one of embodiment one to eight difference:Institute in step 4 The visible light source power stated is the W of 100 W ~ 1000, other steps are identical with embodiment one to eight.
Embodiment ten:Present embodiment is with one of embodiment one to nine difference:Institute in step 5 The external magnetic field strength stated is 0.01T ~ 1T, other steps are identical with embodiment one to nine.
Beneficial effects of the present invention are verified using tests below:
Experiment one:A kind of method that water removal moderate resistance life element is removed using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic
First, persulfuric acid hydrogen salt is mixed with the pretreated water containing antibiotic, then with mixing speed is at room temperature 160 r/min The min of 20 min ~ 45 is stirred under conditions of ~ 250 r/min, obtains the mixed solution of persulfuric acid hydrogen salt and pretreated water;
A kind of antibiotic of step is lavo-ofloxacin;
A kind of persulfuric acid hydrogen salt of step is potassium hydrogen persulfate;
The concentration of antibiotic is 5 mg/L in pretreated water described in step 1:
The mass ratio of the quality of persulfuric acid hydrogen salt described in step 1 and the water of pretreatment is 1:2000;
2nd, adjust pH value in reaction, low whipping speed under conditions of the r/min of 150 r/min~200 using 0.1 mol/L ~ The sodium hydroxide solution of the mol/L of the perchloric acid of 100 mol/L and 0.1 mol/L ~ 100 is by persulfuric acid hydrogen salt and pretreated water The pH values of mixed solution adjust to 6.5 ~ 7.5, the mixing of persulfuric acid hydrogen salt and pretreated water after adjusted pH values is molten Liquid;
3rd, magnetic bismuth oxyiodide is prepared:
1., by Fe3O4Mass fraction is added to as in 97% ~ 99% ethylene glycol, vigorous magnetic stirs 10 min, reuses ultrasonic wave Scattered 30 min of concussion instrument concussion, obtain Fe3O4With the mixed solution of ethylene glycol;
Step 3 1. described in the power of ultrasonic oscillation instrument be 200 W;
Step 3 1. described in Fe3O4Particle diameter be 20 nm;
Step 3 1. described in Fe3O4Quality and the volume ratio of ethylene glycol solution that mass fraction is 97% ~ 99% be 0.01g:1mL;
2., the mixed solution of bismuth nitrate and absolute ethyl alcohol, potassium iodide aqueous solution be added sequentially to Fe3O4With the mixing of ethylene glycol In solution, after 60 min of magnetic agitation, mixing suspension is obtained;
Step 3 2. described in bismuth nitrate and absolute ethyl alcohol mixed solution in the concentration of bismuth nitrate be 1 mol/L;
Step 3 2. described in bismuth nitrate and absolute ethyl alcohol mixed solution and Fe3O4With the volume of the mixed solution of ethylene glycol Than for 10:1;
Step 3 2. described in potassium iodide aqueous solution in the concentration of potassium iodide be 1 mol/L;
Step 3 2. described in potassium iodide aqueous solution and Fe3O4Volume ratio with the mixed solution of ethylene glycol is 10:1;
3., will using the sodium hydroxide solution of the mol/L of the perchloric acid of the mol/L of 0.1 mol/L ~ 100 and 0.1 mol/L ~ 100 Mixing suspension is adjusted to certain ph, then mixing suspension is added to the stainless steel reaction under high pressure that liner is polytetrafluoroethylene (PTFE) In kettle, then stainless steel autoclave sealed, the stainless steel autoclave after sealing is reacted at 120 DEG C ~ 180 DEG C 12h ~ 48h, obtains magnetic bismuth oxyiodide suspension;
Step 3. described in mixing suspension certain ph be pH 7.0;
4., by step 3. in obtained magnetic bismuth oxyiodide suspension in centrifugal speed under the r/min of 6500 r/min ~ 8000 The min of 10 min ~ 30, the deposit after being centrifuged is centrifuged;Deionized water and washes of absolute alcohol is respectively adopted Deposit after centrifugation each 5 times ~ 10 times, the h of then dry 6 h at being -18 DEG C ~ 80 DEG C in temperature ~ 24, obtains magnetic iodine oxygen Change bismuth;
4th, add magnetic bismuth oxyiodide and use radiation of visible light mixed solution;
In persulfuric acid hydrogen salt and the mixed solution of pretreated water that magnetic bismuth oxyiodide is added to after adjusting pH values, reuse Visible light source irradiates mixed solution, and the min of 10 min of reaction time ~ 240, obtains the water containing the bismuth oxyiodide that is magnetic;
The dosage of magnetic bismuth oxyiodide described in step 4 is 10 mg/L;
Visible light source power described in step 4 is 500 W;
5th, magnetic bismuth oxyiodide is separated using external magnetic field:The water containing the bismuth oxyiodide that is magnetic is separated using external magnetic field, is returned Magnetic bismuth oxyiodide is received, the glass fibre membrane that aperture is 0.45 μm is reused and the magnetic bismuth oxyiodide of recycling is filtered, then Respectively using deionized water and absolute ethyl alcohol to respectively cleaning 5 times ~ 10 times of the magnetic bismuth oxyiodide after filtering, then in temperature it is 50 DEG C The h of 12h ~ 48 is dried in vacuo at ~ 75 DEG C, magnetic bismuth oxyiodide after regenerate and removes the plain water of water removal moderate resistance life;
External magnetic field strength described in step 5 is 0.05 T.
The advantages of this experiment:
First, this test operation is simple, and degradation by-products are nontoxic;
2nd, this experiment is to be reacted at normal temperatures and pressures, saves the energy, and the method phase of the antibiotic in water removal is gone with other Than reducing cost 50%;
3rd, the synthesized magnetic bismuth oxyiodide of this experiment can be easier to recycle and regenerate;
4th, this experiment has good removal rate up to 96% to antibiotic in water.
Experiment two:The contrast test of water removal moderate resistance life element is gone using activated carbon, is specifically realized by the following steps:
24 h of antibiotic in pretreated water is adsorbed for the coconut husk granular activated carbon of the nm of 4 nm ~ 100 using particle diameter, is removed The water of antibiotic in water;
Antibiotic is lavo-ofloxacin in the pretreated water, and the concentration of lavo-ofloxacin is 5 mg/L;
Gone in experiment two using particle diameter for antibiotic in the coal quality granular activated carbon Adsorption pretreated water of the nm of 4 nm ~ 100 Except rate is 36%.
Experiment three:The contrast test of water removal moderate resistance life element is gone using potassium permanganate, is specifically realized by the following steps:
Add the potassium permanganate that concentration is 10 mg/L into the water of pretreatment, 2 h of antibiotic in oxidation removal pretreated water, Obtain the water of water removal moderate resistance life element;
Antibiotic is lavo-ofloxacin in the pretreated water, and the concentration of lavo-ofloxacin is 5 mg/L;
Experiment three is 57% using the removal rate that potassium permanganate oxidation removes antibiotic in pretreated water.
Experiment four:The contrast test of water removal moderate resistance life element is gone using potassium hydrogen persulfate, is specifically realized by the following steps:
The potassium hydrogen persulfate of 2 mg/L is added into pretreated water, reacts 2 h, obtains the water of water removal moderate resistance life element;
Antibiotic is lavo-ofloxacin in the pretreated water, and the concentration of lavo-ofloxacin is 5 mg/L;
Experiment four is 2% using the removal rate that potassium hydrogen persulfate removes antibiotic in pretreated water.
Experiment two using cocoanut active charcoal go water removal moderate resistance life element, experiment three using potassium permanganate go water removal moderate resistance life element and It is respectively 36%, 57% and 2% that experiment four removes the removal rate of water removal moderate resistance life element using potassium hydrogen persulfate, and tests one removal rate For 96%, it was demonstrated that experiment one is for removing antibiotic excellent in pretreated water.

Claims (10)

1. a kind of method that water removal moderate resistance life element is removed using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic, its feature are existed Go to remove water the plain method of moderate resistance life using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic to be according to the following steps in a kind of Complete:
First, persulfuric acid hydrogen salt is mixed with the pretreated water containing antibiotic, then with mixing speed is at room temperature 160 r/min The min of 20 min ~ 45 is stirred under conditions of ~ 250 r/min, obtains the mixed solution of persulfuric acid hydrogen salt and pretreated water;
Persulfuric acid hydrogen salt described in step 1 is in potassium hydrogen persulfate, hydrogen persulfate ammonium, hydrogen persulfate sodium and hydrogen persulfate calcium One kind or wherein several mixtures;
The concentration of antibiotic is 0.01~100 mg/L in pretreated water described in step 1:
The mass ratio of the quality of persulfuric acid hydrogen salt described in step 1 and the water of pretreatment is 1:(1000~10000);
2nd, adjust pH value in reaction, low whipping speed under conditions of the r/min of 150 r/min~200 using 0.1 mol/L ~ The perchloric acid of 100 mol/L and the sodium hydroxide solution of 0.1mol/L ~ 100mol/L are by persulfuric acid hydrogen salt and pretreated water The pH values of mixed solution are adjusted to 6.5 ~ 7.5, the mixed solution of persulfuric acid hydrogen salt and pretreated water after adjusted pH values;
3rd, magnetic bismuth oxyiodide is prepared:
1., by Fe3O4Mass fraction is added to as in 97% ~ 99% ethylene glycol, vigorous magnetic stirs 10 min, reuses ultrasonic wave Scattered 30 min of concussion instrument concussion, obtain Fe3O4With the mixed solution of ethylene glycol;
Step 3 1. described in Fe3O4Quality and the volume ratio of ethylene glycol solution that mass fraction is 97% ~ 99% be (0.001g~10g):1 mL;
2., the mixed solution of bismuth nitrate and absolute ethyl alcohol, potassium iodide aqueous solution be added sequentially to Fe3O4With the mixing of ethylene glycol In solution, after 60 min of magnetic agitation, mixing suspension is obtained;
Step 3 2. described in bismuth nitrate and absolute ethyl alcohol mixed solution in the concentration of bismuth nitrate be 0.01 ~ 10 mol/L;
Step 3 2. described in bismuth nitrate and absolute ethyl alcohol mixed solution and Fe3O4With the volume of the mixed solution of ethylene glycol Than for (0.1 ~ 100):1;
Step 3 2. described in potassium iodide aqueous solution in the concentration of potassium iodide be 0.01 ~ 10 mol/L;
Step 3 2. described in potassium iodide aqueous solution and Fe3O4Volume ratio with the mixed solution of ethylene glycol is (0.1 ~ 100): 1;
3., will using the sodium hydroxide solution of the mol/L of the perchloric acid of the mol/L of 0.1 mol/L ~ 100 and 0.1 mol/L ~ 100 Mixing suspension is adjusted to certain ph, then mixing suspension is added to the stainless steel reaction under high pressure that liner is polytetrafluoroethylene (PTFE) In kettle, then stainless steel autoclave sealed, the stainless steel autoclave after sealing is reacted 12 at 120 DEG C ~ 200 DEG C The h of h ~ 48, obtains magnetic bismuth oxyiodide suspension;
Step 3. described in mixing suspension certain ph be pH 1.0 ~ 7.0;
4., by step 3. in obtained magnetic bismuth oxyiodide suspension in centrifugal speed under the r/min of 6500 r/min ~ 8000 The min of 10 min ~ 30, the deposit after being centrifuged is centrifuged;Deionized water and washes of absolute alcohol is respectively adopted Deposit after centrifugation each 5 times ~ 10 times, then dry 6h ~ 24h in the case where temperature is -18 DEG C ~ 80 DEG C, obtain Tan solid As magnetic bismuth oxyiodide;
4th, add magnetic bismuth oxyiodide and use radiation of visible light mixed solution;
In persulfuric acid hydrogen salt and the mixed solution of pretreated water that magnetic bismuth oxyiodide is added to after adjusting pH values, reuse Visible light source irradiates mixed solution, and the min of 10 min of reaction time ~ 240, obtains the water containing the bismuth oxyiodide that is magnetic;
The dosage of magnetic bismuth oxyiodide described in step 4 is the mg/L of 1 mg/L ~ 200;
Visible light source power described in step 4 is the W of 10 W ~ 1000;
5th, magnetic bismuth oxyiodide is separated using external magnetic field:The water containing the bismuth oxyiodide that is magnetic is separated using external magnetic field, is returned Magnetic bismuth oxyiodide is received, the glass fibre membrane that aperture is 0.45 μm is reused and the magnetic bismuth oxyiodide of recycling is filtered, then Cleaned 5 times ~ 10 times using deionized water and absolute ethyl alcohol are each to the magnetic bismuth oxyiodide difference after filtering respectively, then be in temperature 12h ~ 48h is dried in vacuo at 50 DEG C ~ 75 DEG C, the magnetic bismuth oxyiodide after being regenerated and the water for removing water removal moderate resistance life element.
2. one kind according to claim 1 goes water removal moderate resistance using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic The method of raw element, it is characterised in that the antibiotic in pretreated water described in step 1 is lavo-ofloxacin, Ciprofloxacin, promise One or more of mixtures in Flucloxacillin, gatifloxacin and fleraxacin.
3. one kind according to claim 1 goes water removal moderate resistance using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic The method of raw element, it is characterised in that the mass ratio of the quality of the persulfuric acid hydrogen salt described in step 1 and the water of pretreatment is 1: (1000~5000)。
4. one kind according to claim 1 goes water removal moderate resistance using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic The method of raw element, it is characterised in that the mass ratio of the quality of the persulfuric acid hydrogen salt described in step 1 and the water of pretreatment is 1: (5000~8000)。
5. one kind according to claim 1 goes water removal moderate resistance using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic The method of raw element, it is characterised in that step 3 1. described in the power of ultrasonic oscillation instrument be the W of 100 W ~ 1000.
6. one kind according to claim 1 goes water removal moderate resistance using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic The method of raw element, it is characterised in that 1. step 3 plants the Fe3O4Particle diameter be the nm of 15 nm ~ 500.
7. one kind according to claim 1 goes water removal moderate resistance using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic The method of raw element, it is characterised in that 1. step 3 plants the Fe3O4Particle diameter be the nm of 500 nm ~ 2000.
8. one kind according to claim 1 goes water removal moderate resistance using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic The method of raw element, it is characterised in that the dosage of the magnetic bismuth oxyiodide described in step 4 is the mg/L of 1 mg/L ~ 10.
9. one kind according to claim 1 goes water removal moderate resistance using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic The method of raw element, it is characterised in that visible light source power described in step 4 is the W of 100 W ~ 1000.
10. one kind according to claim 1 is gone in water removal using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic The method of antibiotic, it is characterised in that the external magnetic field strength described in step 5 is 0.01T ~ 1T.
CN201711245269.6A 2017-12-01 2017-12-01 A kind of method that water removal moderate resistance life element is removed using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic Pending CN107935102A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201711245269.6A CN107935102A (en) 2017-12-01 2017-12-01 A kind of method that water removal moderate resistance life element is removed using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201711245269.6A CN107935102A (en) 2017-12-01 2017-12-01 A kind of method that water removal moderate resistance life element is removed using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic

Publications (1)

Publication Number Publication Date
CN107935102A true CN107935102A (en) 2018-04-20

Family

ID=61947227

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201711245269.6A Pending CN107935102A (en) 2017-12-01 2017-12-01 A kind of method that water removal moderate resistance life element is removed using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic

Country Status (1)

Country Link
CN (1) CN107935102A (en)

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109433269A (en) * 2018-10-15 2019-03-08 南京大学 A kind of preparation method and application of water-setting matrix bismuth oxyiodide composite catalyst
CN111054399A (en) * 2019-12-10 2020-04-24 武汉纺织大学 Microwave synthesis oxygen vacancy BiOCl/Bi2O3Catalyst and preparation method and application thereof
CN111234295A (en) * 2019-12-05 2020-06-05 太原理工大学 Molecularly imprinted photocatalytic material and preparation method and application thereof
CN111252848A (en) * 2020-02-25 2020-06-09 中国电建集团成都勘测设计研究院有限公司 Using CeO2Method for removing tetracycline hydrochloride in water by catalytically activating sodium persulfate under visible light of composite BiOI material
CN113042072A (en) * 2021-03-15 2021-06-29 西安科技大学 Bismuth oxide/defect bismuth oxyiodide composite material, preparation method and application thereof
CN109126835B (en) * 2018-07-26 2021-09-07 中国电建集团成都勘测设计研究院有限公司 Photocatalyst La3+BiOI and method for degrading bisphenol AF
CN113600173A (en) * 2021-08-09 2021-11-05 中山大学 Application of bismuth catalyst in sterilization and disinfection by activating persulfate
CN114425371A (en) * 2021-12-21 2022-05-03 北京建筑大学 Method for inducing self-assembly of bismuth-based photocatalytic material by biosurfactant and application
CN114804282A (en) * 2022-04-13 2022-07-29 海天水务集团股份公司 Method for photocatalytic degradation of levofloxacin in wastewater
CN115254152A (en) * 2022-06-22 2022-11-01 中国科学技术大学苏州高等研究院 Application of cobalt-doped bismuth oxybromide catalyst in selective oxidative degradation of pollutants

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104667871A (en) * 2015-02-11 2015-06-03 四川大学 Method for eliminating endocrine disrupter in water by activating monopersulfate with ferro-cerium dual-phase loaded graphene oxide
CN104743633A (en) * 2015-04-16 2015-07-01 安徽工业大学 Method for degrading organic waste water by photo-assisted activation of potassium hydrogen persulfate through bismuth ferrite
CN105036292A (en) * 2015-08-19 2015-11-11 河南师范大学 Method for degrading rhodamine B dye wastewater by catalyzing Oxone with magnetic cobalt catalyst
CN106966459A (en) * 2017-05-02 2017-07-21 河南师范大学 The method that magnetic nano-catalyst CoFe PBAs@rGO are catalyzed Oxone degrading organic dye waste waters

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104667871A (en) * 2015-02-11 2015-06-03 四川大学 Method for eliminating endocrine disrupter in water by activating monopersulfate with ferro-cerium dual-phase loaded graphene oxide
CN104743633A (en) * 2015-04-16 2015-07-01 安徽工业大学 Method for degrading organic waste water by photo-assisted activation of potassium hydrogen persulfate through bismuth ferrite
CN105036292A (en) * 2015-08-19 2015-11-11 河南师范大学 Method for degrading rhodamine B dye wastewater by catalyzing Oxone with magnetic cobalt catalyst
CN106966459A (en) * 2017-05-02 2017-07-21 河南师范大学 The method that magnetic nano-catalyst CoFe PBAs@rGO are catalyzed Oxone degrading organic dye waste waters

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
张强等: "可见光催化剂Fe3O4/BiOI的制备及其催化活性研究", 《水污染及处理》 *

Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109126835B (en) * 2018-07-26 2021-09-07 中国电建集团成都勘测设计研究院有限公司 Photocatalyst La3+BiOI and method for degrading bisphenol AF
CN109433269A (en) * 2018-10-15 2019-03-08 南京大学 A kind of preparation method and application of water-setting matrix bismuth oxyiodide composite catalyst
CN111234295A (en) * 2019-12-05 2020-06-05 太原理工大学 Molecularly imprinted photocatalytic material and preparation method and application thereof
CN111234295B (en) * 2019-12-05 2022-06-03 太原理工大学 Molecularly imprinted photocatalytic material and preparation method and application thereof
CN111054399A (en) * 2019-12-10 2020-04-24 武汉纺织大学 Microwave synthesis oxygen vacancy BiOCl/Bi2O3Catalyst and preparation method and application thereof
CN111252848A (en) * 2020-02-25 2020-06-09 中国电建集团成都勘测设计研究院有限公司 Using CeO2Method for removing tetracycline hydrochloride in water by catalytically activating sodium persulfate under visible light of composite BiOI material
CN113042072B (en) * 2021-03-15 2022-04-05 西安科技大学 Bismuth oxide/defect bismuth oxyiodide composite material, preparation method and application thereof
CN113042072A (en) * 2021-03-15 2021-06-29 西安科技大学 Bismuth oxide/defect bismuth oxyiodide composite material, preparation method and application thereof
CN113600173A (en) * 2021-08-09 2021-11-05 中山大学 Application of bismuth catalyst in sterilization and disinfection by activating persulfate
CN114425371A (en) * 2021-12-21 2022-05-03 北京建筑大学 Method for inducing self-assembly of bismuth-based photocatalytic material by biosurfactant and application
CN114804282A (en) * 2022-04-13 2022-07-29 海天水务集团股份公司 Method for photocatalytic degradation of levofloxacin in wastewater
CN114804282B (en) * 2022-04-13 2023-07-25 海天水务集团股份公司 Method for degrading levofloxacin in wastewater by photocatalysis
CN115254152A (en) * 2022-06-22 2022-11-01 中国科学技术大学苏州高等研究院 Application of cobalt-doped bismuth oxybromide catalyst in selective oxidative degradation of pollutants

Similar Documents

Publication Publication Date Title
CN107935102A (en) A kind of method that water removal moderate resistance life element is removed using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic
CN110586038B (en) Biochar loaded nano zero-valent iron material and application thereof
CN101829545B (en) Heavy metal biological adsorbent using eggshell membrane as matrix and preparation method thereof
CN111318254B (en) Preparation method of high-efficiency regenerated activated carbon
CN106474819A (en) A kind of gas filtration cotton containing graphene oxide and preparation method thereof
CN109179554A (en) Utilize the method for fortimicin in manganese dioxide load biological carbon materials removal water body
CN104059167A (en) Preparation method of polyamine compound-modified magnetic chitosan and application thereof
CN112933997B (en) Preparation method and application of inorganic modified membrane based on in-situ reduction
CN113842883B (en) Lanthanum-loaded iron carbon nanotube film material for environmental remediation and preparation method and application thereof
CN110801814A (en) Preparation method of magnetic amino walnut shell biochar novel adsorbent
CN101954272A (en) Trace iodine adsorbent for electrolytic saline solution, preparation method and application thereof
CN107754807A (en) A kind of method that estrogen in water removal is removed using sodium peroxydisulfate and magnetic photocatalyst
CN108339517B (en) Flexible biomass selenium extraction material and preparation method thereof
CN112044398A (en) Application of graphene adsorption material in phenol wastewater treatment
CN112661228A (en) Method for purifying rhodamine B dye wastewater
CN111760558A (en) Preparation method, application and regeneration method of chitosan modified zeolite molecular sieve
CN112473626A (en) Cellulose-based composite adsorbent for wastewater treatment
CN109126900A (en) A kind of light-catalyzed reaction gel mould
CN110420653A (en) A kind of silver orthophosphate/hydro-thermal charcoal composite photo-catalyst and the preparation method and application thereof
CN106362686B (en) A kind of preparation method of the composite material of enrichment degrading benzene object organic wastewater
CN112755961B (en) MgO-loaded activated carbon and preparation method and application thereof
CN107973366A (en) One kind utilizes persulfuric acid hydrogen salt and photochemical catalyst BiVO4The method of purifying dyestuff waste water
CN110975809B (en) Tangerine-based biochar and application thereof
CN112661968B (en) Method for preparing MOF adsorption material
CN102728325A (en) Preparation method of modified ethyl cellulose adsorption material

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
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20180420

WD01 Invention patent application deemed withdrawn after publication