CN107469834A - A kind of ZnS/CuS nanometer sheets composite photo-catalyst preparation method - Google Patents

A kind of ZnS/CuS nanometer sheets composite photo-catalyst preparation method Download PDF

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CN107469834A
CN107469834A CN201710741068.9A CN201710741068A CN107469834A CN 107469834 A CN107469834 A CN 107469834A CN 201710741068 A CN201710741068 A CN 201710741068A CN 107469834 A CN107469834 A CN 107469834A
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zns
cus
preparation
composite materials
nanosheet composite
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CN107469834B (en
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郑小刚
付文娣
黄明
刘敏
刘勇
张金洋
付孝锦
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Neijiang Normal University
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/02Sulfur, selenium or tellurium; Compounds thereof
    • B01J27/04Sulfides
    • B01J35/39
    • 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
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/722Oxidation by peroxides
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • 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
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Abstract

The invention belongs to technical field of nanometer material preparation, specially a kind of preparation method of ZnS/CuS nanosheet composite materials.The method comprising the steps of:1)Raw material nitrate trihydrate copper, zinc nitrate hexahydrate, thiocarbamide and surfactant are weighed in proportion, is then put into acetonitrile solution and carries out ultrasound, constant temperature stirring are then carried out, to form uniform copper zinc mixed solution;2)Above-mentioned solution is fitted into hydrothermal reaction kettle, reacted under specified temperature and time;3)Reaction is completed, and after natural cooling, removes supernatant, is respectively washed three times with deionized water and absolute ethyl alcohol, in an oven 60 DEG C of dry 5h, products obtained therefrom is Cu:Zn=x:Y composite nano plate.Photo-generated carrier can be efficiently separated with during photocatalyst using copper sulfide (CuS)/zinc sulphide (ZnS) bimetallic sulfide in the application, effectively improve photocatalytic activity.

Description

A kind of ZnS/CuS nanometer sheets composite photo-catalyst preparation method
Technical field
The invention belongs to technical field of nanometer material preparation, specially a kind of preparation of ZnS/CuS nanosheet composite materials Method.
Background technology
Water pollutant includes inorganic pollution and organic pollution.Inorganic pollution mainly includes lead, chromium, every, mercury and The heavy metal ion such as copper, these heavy metal elements have in the environment difficult degradation, easily accumulation, irreversible, toxicity is big, metabolism is slow and The characteristics of being easily bioaccumulation.Acute and chronic poisoning can be triggered or cause body canceration by drinking contaminated by heavy metals water for a long time.Have Organic pollutants mainly include oxygen consumption non-toxic organic thing (such as protein, fat and carbohydrate) and toxic organic compound (such as phenol Class compound, organic agricultural chemicals and polycyclic aromatic hydrocarbon, dyestuff and food additives etc.), these organic pollutions be teratogenesis, mutagenesis and Carcinogen.
《National drinking water source water quality plays greatly bottom within 2016》Report is shown, disclosed in 31 provincial environmental administrations in 2016 There are 24 provinces in the water quality condition of (surface water water head site 995, groundwater source field 338) drinking water source area at 1333 Overproof water quality at totally 98, the exceeded ratio of groundwater source is apparently higher than surface water water source, and the duration polluted is compared with the latter more It is long.If preventing and treating and processing speed are unable to catch up with the speed of pollution, drinking water pollution is just difficult to be contained.
At present, the means such as generally use chemical method, physical-chemical process and biotechnology processing water pollutant.
The removal of heavy metal ion is mainly chemical precipitation method, and principle is to make to be in ion like in waste water by chemical reaction The heavy metal of state is converted into sediment not soluble in water, is then separated from waste liquid sediment by filtering, including ammonia Oxide precipitation method, sulphide precipitation, calcium salt precipitation method and ferrite coprecipitation etc..The shortcomings that this method is after handling Waste liquid does not often reach discharge standard, and if caused sediment deal with improperly, easily cause secondary pollution.To organic dirt The removal for contaminating thing is typically chemical degradation method, mainly utilizes photocatalytic oxidation, wet oxidation process, supercritical water oxidation method electricity Chemical oxidization method, Ozonation harmony chemical degradation etc., make organic pollution oxidation Decomposition and be converted into avirulent give birth to Change degradation material, this method is to administer the effective ways of persistence organic pollutant.
Physical-chemical process mainly includes absorption method, ion-exchange and membrane separation process.Absorption is existing for solid-liquid interface A kind of universal phenomenon, utilize the heavy metal ion in the loose porous and big adsorbent absorption effluent of specific surface area and organic contamination Thing, to reach the purpose of purified water.Ion-exchange is to be carried out by means of the cation exchange groups in exchanger with the ion in waste water Exchange, so as to remove the harmful ion in waste water.Membrane separation process be certain motive force effect under, it is saturating using the selection of pellicle The property crossed is separated and concentrated, and common membrane separation process includes electroosmose process, diffusive dialysis method, hyperfiltration and ultrafiltration etc.. It is higher to manufacturing requirements because its program is complicated, it is restricted in popularization and application.
Biotechnology includes phytoremediation technology and microorganism remediation technology.Phytoremediation technology, grown using nature Or the plant cultivated of genetic engineering and its microorganism system coexists, excessive accumulaiton certain or some pollutants, remove in environment Pollutant.The mode of phytoremediation includes plant extract, plant degradation, plant stability and phytovolatilization etc..Microorganism remediation skill Art, it is using the naturally occurring or functional microorganism group that manually cultivates, is absorbed under the conditions of control environment or poisonous dirt of degrading Contaminate thing.The technology shows its high efficiency, low cost and non-secondary pollution in terms of heavy metal pollution and organic pollution is administered Etc. advantage, turn into one of focus studied in environmental organism recovery technique field.
In above processing method, photocatalytic oxidation is because its treatment effect is high, the reaction time is short, easy to operate and be not easy The advantages that causing secondary pollution, particularly contaminative is strong, low concentration, other processing methods be difficult to effectively to handle it is heavy metal-polluted Dye and organic polluting water field have special application value.Conventional photochemical catalyst includes titanium dioxide (TiO2), oxidation Zinc (ZnO), tin oxide (SnO2), zirconium dioxide (ZrO2), many oxide sulfide semiconductor such as cadmium sulfide (CdS), wherein two Titanium oxide because its oxidability is strong, stablize nontoxic, turns into nano photocatalyst catalytic material most hot in the world by chemical property, but due to Its band-gap energy is higher, it is relatively low to solar energy utilization ratio the shortcomings of, therefore be difficult to realize photocatalytic degradation under visible light conditions.In morning It is phase, also once more to use cadmium sulfide (CdS) and zinc oxide (ZnO) to be used as photocatalyst material, but due to the chemistry of both Property is unstable, can be light-catalysed while light dissolving occurs, and the harmful metal ion of dissolution has certain bio-toxicity, sent out Seldom used them as at present as civilian catalysis material up to national, so cheap, the efficient nano-photocatalyst of exploitation It is an importance of current absorption research.
The content of the invention
The goal of the invention of the present invention is to overcome problem above, there is provided a kind of preparation of ZnS/CuS nanosheet composite materials Method.This method with nano combined of CuS nanoparticles/ZnS for photochemical catalyst, using the rhodamine B of difficult degradation and low cost to handle Agent, improve application of the inorganic composite nano material in light degradation field.
In order to realize above goal of the invention, concrete technical scheme of the invention is as follows:
A kind of preparation method of the compound composite of ZnS/CuS nanometer sheets, it comprises the following steps:
1)Raw material nitrate trihydrate copper, zinc nitrate hexahydrate, thiocarbamide and surfactant are weighed in proportion, are then put into acetonitrile water It is ultrasonically treated in solution, and constant temperature stirs, to form uniform copper zinc mixed solution;Nitrate trihydrate copper, zinc nitrate hexahydrate Mass ratio with thiocarbamide is 0.1 ~ 3g:0.1~4g:0.2~5g.The quality of thiocarbamide and the volume ratio of acetonitrile solution are 0.2 ~ 5g:50- 200mL;The concentration of acetonitrile solution is 50wt%.
2)Above-mentioned solution is fitted into hydrothermal reaction kettle, reacted under specified temperature and time;
3)Reaction is completed, and after natural cooling, removes supernatant, is respectively washed three times, in baking oven with deionized water and absolute ethyl alcohol In 60 DEG C of dry 5h, products obtained therefrom is Cu:Zn=x:Y composite nano plate.
Described surfactant is lauryl sodium sulfate, the polyethylene glycol of Mw=10000, the poly- second two of Mw=20000 Alcohol, neopelex, Mw=58000 polyvinylpyrrolidone and cetyl trimethylammonium bromide in it is any one Kind or several mixtures.
The step 1)The condition of middle constant temperature stirring is:25 ~ 35 DEG C, 100 ~ 400r/min of stirring intensity of temperature, during stirring Between 30 ~ 150min.
The condition of ultrasound:50 ~ 99Hz of intensity, 20 DEG C ~ 50 DEG C of temperature, 5 ~ 20min of time;
Step 2)Described in hydrothermal reaction condition be:150 ~ 250 DEG C of temperature, 4 ~ 10h of time.
The positive effect of the present invention is embodied in:
(One)Copper sulfide (CuS)/zinc sulphide (ZnS) bimetallic sulfide can efficiently separate photo-generated carrier, as light Catalyst, it can improve efficiency of light absorption and photocatalytic activity.
(Two)The application with nano combined of CuS nanoparticles/ZnS for photochemical catalyst, with difficult degradation and the rhodamine B of low cost For inorganic agent, application of the inorganic composite nano material in light degradation field is improved.
Brief description of the drawings
Fig. 1 is that CuS/ZnS mol ratios are 1:CuS and ZnS are detected in 1 CuS/ZnS nanosheet composite material XRD spectrums The characteristic diffraction peak of phase.
Fig. 2 is CuS/ZnS nanosheet composite materials(CuS/ZnS mol ratios 1:2)EDX collection of illustrative plates
The elements such as Cu, Zn and S are detected in collection of illustrative plates, this shows that the nanosheet composite material of synthesis is made up of these three elements, water Thermal synthesis method can synthesize CuS/ZnS composites.
Fig. 3 a are CuS/ZnS nanosheet composite materials(CuS/ZnS mol ratios 1:2)SEM figure, its medium scale be 1 μm.
Fig. 3 b are CuS/ZnS nanosheet composite materials(CuS/ZnS mol ratios 1:2)SEM figures, its medium scale is 200nm。
Fig. 4 a are CuS/ZnS nanosheet composite materials(CuS/ZnS mol ratios 1:4)SEM figure, its medium scale be 1 μm;
Fig. 4 b are CuS/ZnS nanosheet composite materials(CuS/ZnS mol ratios 1:4)SEM figure, its medium scale is 200nm;
Fig. 5 a are CuS/ZnS(CuS/ZnS mol ratios 3:1)The SEM figures of nanosheet composite material, its medium scale are 1 μm;
Fig. 5 b are CuS/ZnS(CuS/ZnS mol ratios 3:1)The SEM figures of nanosheet composite material, its medium scale is 200nm;
Fig. 6 a are CuS/ZnS(CuS/ZnS mol ratios 4:1)The SEM figures of nanosheet composite material, its medium scale are 1 μm;
Fig. 6 b are CuS/ZnS(CuS/ZnS mol ratios 4:1)The SEM figures of nanosheet composite material, its medium scale is 200nm.
Embodiment:
In order to make the purpose , technical scheme and advantage of the present invention be clearer, with reference to embodiment to this hair It is bright to be described in further detail, but the scope that this should not be interpreted as to the above-mentioned theme of the present invention is only limitted to following embodiments.
Embodiment 1:
Weigh 0.322g nitrate trihydrates copper, 0.7934g zinc nitrate hexahydrates, 0.6976g thiocarbamides, 0.1g polyvinylpyrrolidones(Mw= 58000)Add in volume 160mL, mass fraction 50wt% acetonitrile mixed solution, ultrasonic 5min, and low whipping speed is 60min is stirred under 500r/min normal temperature and forms copper zinc mixed solution, above-mentioned solution is fitted into polytetrafluoroethylene (PTFE) pyroreaction kettle, In 200 DEG C of hydro-thermal reaction 6h, after natural cooling, remove supernatant, respectively washed three times with deionized water and absolute ethyl alcohol, and 60 DEG C of dry 5h in an oven, products obtained therefrom are that CuS/ZnS mol ratios are 1:2 composite nano plate.
Embodiment 2:
0.1932g nitrate trihydrates copper, 0.9520g zinc nitrate hexahydrates, 0.6976g thiocarbamides, 0.1g PEG 20000s is weighed to add to Volume 140mL, mass fraction 50wt% acetonitrile mixed solution in, ultrasonic 5min, and low whipping speed be 500r/min normal temperature under Stir 60min and form copper zinc mixed solution, above-mentioned solution is fitted into polytetrafluoroethylene (PTFE) pyroreaction kettle, it is anti-in 200 DEG C of hydro-thermals 5h is answered, after natural cooling, removes supernatant, is respectively washed three times with deionized water and absolute ethyl alcohol, 60 DEG C of dryings in an oven 5h, products obtained therefrom are that CuS/ZnS mol ratios are 1:4 composite nano plate.
Embodiment 3:
Weigh 0.7248g nitrate trihydrates copper, 0.2974g zinc nitrate hexahydrates, 0.6976g thiocarbamides, 0.1g neopelexes Add in 150mL, mass fraction 60wt% acetonitrile mixed solution, ultrasonic 5min, and low whipping speed is under 500r/min normal temperature Stir 60min and form copper zinc mixed solution, above-mentioned solution is fitted into polytetrafluoroethylene (PTFE) pyroreaction kettle, it is anti-in 190 DEG C of hydro-thermals 8h is answered, after natural cooling, removes supernatant, is respectively washed three times with deionized water and absolute ethyl alcohol, 60 DEG C of dryings in an oven 5h, products obtained therefrom are that CuS/ZnS mol ratios are 3:1 composite nano plate.
Embodiment 4:
Weigh 0.9664g nitrate trihydrates copper, 0.2974g zinc nitrate hexahydrates, 0.6976g thiocarbamides, 0.1g neopelexes Added to 0.05g cetyl trimethylammonium bromides in 160mL, mass fraction 45wt% acetonitrile mixed solution, ultrasonic 5min, And low whipping speed is to stir 60min under 500r/min normal temperature to form copper zinc mixed solution, and above-mentioned solution is loaded into polytetrafluoroethyl-ne In alkene pyroreaction kettle, in 190 DEG C of hydro-thermal reaction 8h, after natural cooling, remove supernatant, with deionized water and anhydrous second Respectively three times, 60 DEG C of dry 5h, products obtained therefrom are that CuS/ZnS mol ratios are 4 to alcohol in an oven for washing:1 composite nano plate.
It is 1 to weigh the CuS/ZnS mol ratios being prepared in 0.15g above-described embodiments respectively:2、1:4、3:1 and 4:1 Nanosheet composite material is used as visible region(400W xenon lamps)Volume of degrading 100mL, concentration 20mg/L rhodamine B solution, Under the radiation that 20 μ L hydrogen peroxide participate in after 2h, CuS/ZnS mol ratios are measured as 1:2、1:4、3:1 and 4:1 nanometer sheet is answered Condensation material is respectively to the degradation rate of rhodamine B solution:97.2%th, 78.3%, 80.0% and 86.5%.ZnS under the same terms and CuS is respectively 70.1% and 73.4% to the degradation rate of rhodamine B solution.This shows that the light of CuS/ZnS nanosheet composite materials is urged Change photocatalysis performance when activity is higher than ZnS and CuS independent roles.

Claims (7)

1. a kind of preparation method of ZnS/CuS nanosheet composite materials, it is characterised in that comprise the following steps:
1)Raw material nitrate trihydrate copper, zinc nitrate hexahydrate, thiocarbamide and surfactant are weighed in proportion, are put into acetonitrile solution It is middle to carry out ultrasound, constant temperature stirring is then carried out, to form uniform copper zinc mixed solution;
2)Above-mentioned solution is fitted into hydrothermal reaction kettle, reacted under specified temperature and time;
3)Reaction is completed, and after natural cooling, removes supernatant, is respectively washed three times, in baking oven with deionized water and absolute ethyl alcohol In 60 DEG C of dry 5h, products obtained therefrom is Cu:Zn=x:Y composite nano plate.
2. the preparation method of ZnS/CuS nanosheet composite materials according to claim 1, it is characterised in that:Nitrate trihydrate copper, The mass ratio of zinc nitrate hexahydrate and thiocarbamide is 0.1 ~ 3g:0.1~4g:0.2~5g.
3. the preparation method of ZnS/CuS nanosheet composite materials according to claim 1, it is characterised in that:The quality of thiocarbamide Volume ratio with acetonitrile solution is 0.2 ~ 5g:50-200mL;The concentration of acetonitrile solution is 50wt%.
4. the preparation method of ZnS/CuS nanosheet composite materials according to claim 1, it is characterised in that:Described surface Activating agent is lauryl sodium sulfate, the polyethylene glycol of Mw=10000, the polyethylene glycol of Mw=20000, DBSA Sodium, Mw=58000 polyvinylpyrrolidone and cetyl trimethylammonium bromide in any one or a few mixture.
5. the preparation method of ZnS/CuS nanosheet composite materials according to claim 1, it is characterised in that the step 1)In Constant temperature stirring condition be:25 ~ 35 DEG C, 100 ~ 400r/min of stirring intensity, 30 ~ 150min of mixing time of temperature.
6. the preparation method of ZnS/CuS nanosheet composite materials according to claim 1, it is characterised in that:It is described ultrasonic Condition is:50 ~ 99Hz of intensity, 20 DEG C ~ 50 DEG C of temperature, 5 ~ 20min of time.
7. the preparation method of ZnS/CuS nanosheet composite materials according to claim 1, it is characterised in that step 2)Described in Hydrothermal reaction condition be:150 ~ 250 DEG C of temperature, 4 ~ 10h of time.
CN201710741068.9A 2017-08-25 2017-08-25 Preparation method of ZnS/CuS nanosheet composite photocatalyst Expired - Fee Related CN107469834B (en)

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CN108940376A (en) * 2018-07-25 2018-12-07 广州大学 A kind of surface organic complex copper sulfide fenton catalyst and its synthetic method and application
CN109012701A (en) * 2018-09-18 2018-12-18 张玉英 It is a kind of for handling the zinc sulphide bronzing catalyst and preparation method of dyeing waste water
CN109368686A (en) * 2018-10-18 2019-02-22 温州大学新材料与产业技术研究院 A kind of hydrothermal synthesis prepares the method and ZnS/CuS heterojunction structure of ZnS/CuS heterojunction structure
CN110739103A (en) * 2018-10-17 2020-01-31 嘉兴学院 Preparation method of CuS/ZnS composite conductive films
CN110773197A (en) * 2019-10-29 2020-02-11 李平 Two-dimensional bimetallic sulfide nanosheet photocatalyst and preparation method thereof
CN111167479A (en) * 2020-03-11 2020-05-19 四川轻化工大学 Preparation method of quaternary visible light catalytic nano composite material
CN114649532A (en) * 2022-03-10 2022-06-21 中国地质大学(武汉) Nest-shaped CuS-Zn lithium ion battery cathode material and preparation method thereof

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CN108940376A (en) * 2018-07-25 2018-12-07 广州大学 A kind of surface organic complex copper sulfide fenton catalyst and its synthetic method and application
CN108940376B (en) * 2018-07-25 2021-06-25 广州大学 Surface organic complexing copper sulfide Fenton catalyst and synthetic method and application thereof
CN109012701A (en) * 2018-09-18 2018-12-18 张玉英 It is a kind of for handling the zinc sulphide bronzing catalyst and preparation method of dyeing waste water
CN109012701B (en) * 2018-09-18 2021-10-19 张玉英 Zinc sulfide copper photocatalyst for treating printing and dyeing wastewater and preparation method thereof
CN110739103A (en) * 2018-10-17 2020-01-31 嘉兴学院 Preparation method of CuS/ZnS composite conductive films
CN110739103B (en) * 2018-10-17 2020-11-03 嘉兴学院 Preparation method of CuS/ZnS composite conductive film
CN109368686A (en) * 2018-10-18 2019-02-22 温州大学新材料与产业技术研究院 A kind of hydrothermal synthesis prepares the method and ZnS/CuS heterojunction structure of ZnS/CuS heterojunction structure
CN109368686B (en) * 2018-10-18 2021-05-21 温州大学新材料与产业技术研究院 Method for preparing ZnS/CuS heterostructure through hydrothermal synthesis and ZnS/CuS heterostructure
CN110773197A (en) * 2019-10-29 2020-02-11 李平 Two-dimensional bimetallic sulfide nanosheet photocatalyst and preparation method thereof
CN111167479A (en) * 2020-03-11 2020-05-19 四川轻化工大学 Preparation method of quaternary visible light catalytic nano composite material
CN114649532A (en) * 2022-03-10 2022-06-21 中国地质大学(武汉) Nest-shaped CuS-Zn lithium ion battery cathode material and preparation method thereof
CN114649532B (en) * 2022-03-10 2024-04-02 中国地质大学(武汉) Nest CuS-Zn lithium ion battery cathode material and preparation method thereof

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