CN106315741A - Method for removing methylene blue from dye wastewater - Google Patents

Method for removing methylene blue from dye wastewater Download PDF

Info

Publication number
CN106315741A
CN106315741A CN201610902230.6A CN201610902230A CN106315741A CN 106315741 A CN106315741 A CN 106315741A CN 201610902230 A CN201610902230 A CN 201610902230A CN 106315741 A CN106315741 A CN 106315741A
Authority
CN
China
Prior art keywords
methylene blue
moo
particle
waste water
dyestuff
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
CN201610902230.6A
Other languages
Chinese (zh)
Inventor
李忠成
马娇娇
王德宝
宋彩霞
牟红宇
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.)
Qingdao University of Science and Technology
Original Assignee
Qingdao University of Science and 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 Qingdao University of Science and Technology filed Critical Qingdao University of Science and Technology
Priority to CN201610902230.6A priority Critical patent/CN106315741A/en
Publication of CN106315741A publication Critical patent/CN106315741A/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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • 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
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • 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
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/16Regeneration of sorbents, filters

Landscapes

  • Chemical & Material Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Organic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (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 relates to a method for removing methylene blue from dye wastewater. Specifically, methylene blue in the dye wastewater can be effectively absorbed and removed through alpha-MoO3 particles under room temperature. According to the invention, alpha-MoO3 particles are prepared by taking (NH4)6Mo7O24.4H2O as precursor and baking at high temperature; the methylene blue solution with the concentration of 1-800mg/L can be absorbed; no by-product is generated; the alpha-MoO3 particles can be reused.

Description

A kind of method removing waste water from dyestuff Methylene Blue
Technical field
The present invention relates to a kind of method removing waste water from dyestuff Methylene Blue, specifically by α-MoO3Particle room The lower efficient absorption of temperature removes the methylene blue in waste water from dyestuff, belongs to the preparation and application field of adsorbent.
Background technology
Methylene blue, also known as methylene blue, methylene blue, alkalescence acid blue, is the heteroaromatic compound of a kind of phenothiazine salt. Methylene blue is the cationic organic dyestuff of industrial normal use, is widely used in weaving, leather, papermaking, dyestuff, plastics etc. Field.At present, the field such as industrial papermaking, chemical industry, dyeing and weaving produces a large amount of waste water dyestuffs, causes environmental pollution, water plant light Close ability to function decline, mankind's Nausea and vomiting, cancerous lesion.Therefore, along with the continuous enhancing of environmental consciousness, sub-containing Organic substance The dye wastewater treatment of methyl blue is of great interest.
In dyeing waste water, dye molecule contains substantial amounts of polar group, and main minimizing technology has: membrance separation, photocatalytic degradation And absorption.Membrane separation process refers to that waste water, by having selective semipermeable membrane, using gradient difference as the power separated, utilizes organic Thing molecule and the particle diameter difference of hydrone, it is achieved dye molecule separates with water.The method has that energy consumption is low, selectivity good, dirty Contaminate the advantages such as little, but operating cost is high, easily occur the shortcomings such as blocking to constrain its application.Photocatalytic oxidation is to utilize quasiconductor Material is catalyst, under light illumination the organic matter degradation in waste water from dyestuff is converted into CO2、H2O, inorganic salt etc. to environment without The material of evil.This technology low energy consumption, non-secondary pollution, be a kind of cleaning, efficient governing measure, but use in photocatalytic process The uviol lamp life-span short, costly, limit its industrial applications.Absorption method is by adsorbent big for surface energy and waste water dyestuff Contact, utilizes the approach such as Van der Waals force, chemical bond, by the Adsorption of Organic in waste water to surface, it is achieved water quality is clean Change.From the point of view of environmental friendliness and reaction efficiency, for processing the dyestuff being difficult to degrade, toxicity is the biggest in waste water, inhale Attached method has preferable advantage, owing to adsorbent is water insoluble, it is easy to collect, and reaches to separate and the purpose of enrichment pollutant.Cause This, utilize adsorption technology to remove waste water dyestuff, owing to its low cost, efficiency are high, simple to operate, have in water treatment field wide Application prospect.
At present, active adsorption waste water from dyestuff is concentrated mainly on activated carbon and material with carbon element system.Such as: Zhang etc. report Graphene oxides nanometer sheet at room temperature absorption property to methylene blue, finds when methylene blue concentration is 15mg/L The highest, removal efficiency is 95% (Z.J.Zhang, et al., RSC Adv., 2015,5,27,922 27932).Zhou etc. report Mesoporous carbon micron ball is at H2O2、NH2Under OH system, when adsorption concentration is the methylene blue solution of 40mg/L, 30 DEG C of contacts The removable methylene blue of 40min.(L.C.Zhou,et al.,Appl.Mater.Interfaces,2014,6,7275-7285). The report activated carbon such as Huang at room temperature can methylene blue in efficient absorption waste water, maximum equilibrium adsorption capacity is 581.4mg/L (H.Huang, et al., Ind.Eng.Chem.Res., 2013,52,14297-14303).
Although these carbon-bearing adsorbents can be with the methylene blue dye in efficient removal waste water reusable edible, but carbon material Expecting expensive, processing cost is higher, regeneration difficulty, is not suitable for the process of high density pollution thing, limits its commercial Application.Mesh Before, the research to adsorbent is concentrated mainly on efficient, the multi-functional and adsorbent of low cost of searching.Metal-oxide is as a class Novel absorption material attracts attention, and goes a good appetite suddenly appearing in a serious disease to show the performance of excellence at the dyestuff such as methyl orange, methylene blue (J.R.Chen,et al.,Appl.Surf.Sci.,2016,378,80–86;A.L.Meng,et al.,ACS Appl.Mater.Interfaces 2015,7,27449-27457).But about effective for waste water dyestuff of molybdenum oxide material There is not been reported for Adsorption, therefore, and research molybdenum oxide material controlledly synthesis and regulation and control so that it is can highly active absorption waste water In methylene blue, there is certain practical value.
Summary of the invention:
It is desirable to provide one is with α-MoO3Particle is the method that adsorbent removes waste water from dyestuff Methylene Blue, can α-the MoO of control synthesis3Particle can remove the methylene blue in waste water with efficient absorption, it is achieved the clearance of 100%.
Based on above-mentioned purpose, technical scheme involved in the present invention is as follows:
1)α-MoO3The preparation of particle: by the ammonium molybdate ((NH of commercialization4)6Mo7O24·4H2O) it is placed in Muffle furnace, It is raised to 500 DEG C from room temperature under air atmosphere, and keeps 4h in this temperature, obtain α-MoO3Particle, particle diameter is about 0.6-3.1 μ m。
2) by α-MoO3Particle is for the adsorption treatment of waste water from dyestuff Methylene Blue.α-MoO3Particle at room temperature adsorbs Methylene blue concentration is the waste water of 1-800mg/L, and adsorption time is 0.5-12h, and methylene blue adsorption number clearance is 100%.
3) by α-MoO3Particle, for the waste water from dyestuff adsorption treatment of 100mg/L methylene blue, after absorption terminates, is isolated Adsorbent, places it in Muffle furnace, is raised to 500 DEG C from room temperature in air atmosphere, and keeps 2h in this temperature, removes absorption Organic substance, adsorbent α-MoO3Particle restores, and has carried out 4 circulation experiments altogether, and 4 times adsorption experiment methylene blue in waste is gone Except rate is 100%.
Relative to current existing adsorbent, present invention have the advantage that
1) by controlledly synthesis α-MoO3Particle, it is achieved that effective removing of waste water solution Methylene Blue, Adsorption Rate is 100%.
2) the adsorbent scope of this adsorbing and removing experiment has effectively been expanded so that it is be no longer mainly limited to carbonaceous material, α-MoO3Particle also can remove the methylene blue in waste water from dyestuff by efficient absorption.
3) present invention has environmental friendliness, process efficiency is high, reuse and feature that its absorption property is sufficiently stable.
Accompanying drawing illustrates:
Fig. 1 is α-MoO3The characterization result of particle.Being characterized by XRD, Raman and Electronic Speculum, obtained material is particle diameter α-MoO for 0.6-3.1 μm3Particle.
Detailed description of the invention
The following example is used for further illustrating the present invention, but does not thereby limits the invention.
Embodiment 1
α-MoO3The preparation of particle:
By the ammonium molybdate ((NH of 10g commercialization4)6Mo7O24·4H2O) put into evaporating dish, place it in Muffle furnace, at sky It is raised to 500 DEG C with 5 DEG C/min from room temperature under gas atmosphere, and keeps 4h in this temperature, finally, under air atmosphere, be naturally down to room Temperature, obtains α-MoO3Particle.
Embodiment 2-13
Material prepared by embodiment 1 is for adsorbing the methylene blue in waste water solution.Adsorption experiment is in the dark carried out, anti- The only impact of illumination.By the α-MoO of 0.4g commercialization3Be respectively 10 with 100mL concentration, 20,40,60,80,100,150,200, 300,400,500, the methylene blue solution of 600mg/L join in 250mL conical flask, this system is stirred at room temperature absorption Certain time (0.5-12h), after absorption, solution centrifugal separates and takes supernatant, with spectrophotometer Perkin Elmer Lambda 750 measures absorbance at methylene blue characteristic absorption wavelength 664nm, analyzes its composition, and correlated results is shown in Table 1.
Table 1 α-MoO3The reaction result of particle absorption Methyl Thionine Chloride in Aqueous
As can be seen from Table 1: α-MoO3Particle can be with the methylene blue in efficient absorption waste water dyestuff.When methylene blue is dense Spending for adsorbing 0.5h during 10mg/L, clearance is 100%.When concentration be 20,40,60,80,100,150,200mg/L time absorption 2.5h, clearance is 100%.When concentration be 300,400,500,600mg/L time absorption 12h, clearance is 100%.
Embodiment 14
Experimental procedure, with embodiment 7, after absorption terminates, separating adsorbent from solution, places it in Muffle furnace, at sky It is raised to 500 DEG C with 5 DEG C/min from room temperature under gas atmosphere, and keeps 2h in this temperature, finally, under air atmosphere, be naturally down to room Temperature, the organic matter removal of absorption, adsorbent α-MoO3Particle restores.Repeat the experimental procedure of embodiment 7, carry out 4 weights altogether Multiple experiment.Adsorption experiment circulates 4 times, and methylene blue in waste clearance is 100%.
Comparative example 1
By the α-MoO of commercialization3Adsorbent as a comparison, experimental procedure is with embodiment 7.Adsorption experiment is in the dark carried out, Prevent the impact of illumination.By the α-MoO of 0.4g commercialization3Join with the methylene blue solution that 100mL concentration is 100mg/L In 250mL conical flask, this system being stirred at room temperature absorption 2.5h, after absorption, solution centrifugal separates and takes supernatant, with dividing Light photometer Perkin Elmer Lambda 750 measures absorbance at methylene blue characteristic absorption wavelength 664nm, finds molten Liquid Methylene Blue eliminating rate of absorption is 25%.

Claims (4)

1. the method removing waste water from dyestuff Methylene Blue, specifically by α-MoO3Efficient absorption under particle room temperature Remove the methylene blue in waste water from dyestuff.
The most in accordance with the method for claim 1, it is characterised in that:
α-MoO3Particle is prepared by following steps:
By the ammonium molybdate ((NH of commercialization4)6Mo7O24·4H2O) it is placed in Muffle furnace, is raised to 400-from room temperature in air atmosphere 600 DEG C, and keep 1-6h in this temperature, obtain α-MoO3Particle, particle diameter is 0.6-3.1 μm.
3. according to the method described in claim 1-2, it is characterised in that: adsorption temp is 20-60 DEG C, and methylene blue concentration is 1- 800mg/L。
4. according to the method described in claim 1-3, it is characterised in that:
α-MoO3Particle adsorbs 0.5-24h at 20-60 DEG C, and absorbing dye methylene blue in waste clearance is 100%.
CN201610902230.6A 2016-10-17 2016-10-17 Method for removing methylene blue from dye wastewater Pending CN106315741A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610902230.6A CN106315741A (en) 2016-10-17 2016-10-17 Method for removing methylene blue from dye wastewater

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610902230.6A CN106315741A (en) 2016-10-17 2016-10-17 Method for removing methylene blue from dye wastewater

Publications (1)

Publication Number Publication Date
CN106315741A true CN106315741A (en) 2017-01-11

Family

ID=57818133

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610902230.6A Pending CN106315741A (en) 2016-10-17 2016-10-17 Method for removing methylene blue from dye wastewater

Country Status (1)

Country Link
CN (1) CN106315741A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106976909A (en) * 2017-01-19 2017-07-25 青岛科技大学 A kind of hexagonal phase h MoO3The preparation method and photocatalytic applications of micron bar
CN107021523A (en) * 2017-01-19 2017-08-08 青岛科技大学 A kind of orthorhombic phase α MoO3The preparation method and its photocatalytic applications of nanobelt
CN112742348A (en) * 2020-12-25 2021-05-04 合肥学院 Waste plastic-based porous activated carbon composite material, preparation method thereof and application thereof in purification of VOCs (volatile organic compounds)
CN113952948A (en) * 2021-11-19 2022-01-21 常州大学 Molybdenum oxide catalyst for preparing cyclohexanediol by oxidizing cyclohexene and preparation method and application thereof
CN114471442A (en) * 2021-12-20 2022-05-13 广东省科学院资源利用与稀土开发研究所 Nano dye wastewater adsorption material and preparation method thereof

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104492420A (en) * 2014-12-19 2015-04-08 北京林业大学 Preparation method of composite catalyst for dye wastewater wet-type catalytic oxidation
CN104998605A (en) * 2015-07-07 2015-10-28 三峡大学 Decoloring agent and synthesis method therefor

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104492420A (en) * 2014-12-19 2015-04-08 北京林业大学 Preparation method of composite catalyst for dye wastewater wet-type catalytic oxidation
CN104998605A (en) * 2015-07-07 2015-10-28 三峡大学 Decoloring agent and synthesis method therefor

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
杨华博 等: "MO3改性的TiO2在可见光下催化降解亚甲基蓝", 《催化学报》 *

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106976909A (en) * 2017-01-19 2017-07-25 青岛科技大学 A kind of hexagonal phase h MoO3The preparation method and photocatalytic applications of micron bar
CN107021523A (en) * 2017-01-19 2017-08-08 青岛科技大学 A kind of orthorhombic phase α MoO3The preparation method and its photocatalytic applications of nanobelt
CN112742348A (en) * 2020-12-25 2021-05-04 合肥学院 Waste plastic-based porous activated carbon composite material, preparation method thereof and application thereof in purification of VOCs (volatile organic compounds)
CN113952948A (en) * 2021-11-19 2022-01-21 常州大学 Molybdenum oxide catalyst for preparing cyclohexanediol by oxidizing cyclohexene and preparation method and application thereof
CN114471442A (en) * 2021-12-20 2022-05-13 广东省科学院资源利用与稀土开发研究所 Nano dye wastewater adsorption material and preparation method thereof

Similar Documents

Publication Publication Date Title
CN106315741A (en) Method for removing methylene blue from dye wastewater
CN110026225B (en) In-NH with visible light catalytic activity2/g-C3N4Composite material and use thereof
CN106362785B (en) A kind of preparation method being acidified azotized carbon nano piece graphene composite aerogel
CN109012724B (en) CoMoO4/g-C3N4Composite photocatalyst and preparation method and application thereof
Wahby et al. Mercury removal from aqueous solution by adsorption on activated carbons prepared from olive stones
CN106040162B (en) A kind of surface modified silicon dioxide material and its preparation method and application
CN104923161A (en) Preparation method of magnetic graphene oxide and application thereof
CN110102267A (en) A kind of aluminium base MOFs/ chitosan compound microsphere and its preparation method and application
CN109012565A (en) A kind of method of the magnetic carbon material Adsorption heavy metal ions in wastewater of nitrating
CN111330648A (en) MIL-101(Fe)/g-C3N4Composite visible light photocatalyst and preparation method and application thereof
CN110354832A (en) Regeneration method of active carbon
CN105597775A (en) Graphene /Cu-Mn-Ce compound catalyst, and preparation method and applications thereof
CN106044744A (en) Preparation method and application of graphene-lignin-based composite hierarchical pore carbon plate material
CN105833666A (en) VOCs waste gas treatment method
KR20200039326A (en) Porous carbon made from plastics and a method for producing the same
CN108671886A (en) A kind of magnetic active carbon adsorbent and the preparation method and application thereof based on abandoned biomass
Zhang et al. Preparation of biochar adsorbent from straw and its adsorption capability
Zhen et al. Decontamination of methylene blue from aqueous solution by rhamnolipid-modified biochar
Rabieh et al. Clew-like hierarchical ZnO nanostructure assembled by nanosheets as an efficient photocatalyst for degradation of azure B
CN107349905A (en) The method that a kind of nitrogen co-doped magnetic carbon material of fluorine removes hexavalent chromium in industrial wastewater
CN106390924A (en) Method for preparing vermiculite/activated carbon based water treatment agent
CN113042018A (en) Preparation method and application of calcium-rich biochar
CN108772038A (en) The adsorbent and its preparation method and application of lead ion in a kind of removing water
CN111036299B (en) Catalytic material for targeted removal of phthalate pollutants based on MIL-100 carbide and preparation method and application thereof
CN106039995A (en) Integrated VOCs adsorption concentration-catalytic oxydative degradation turning wheel device and process thereof

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
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20170111