CN104276619B - A kind of method for the treatment of of dyeing and printing Methylene Blue - Google Patents

A kind of method for the treatment of of dyeing and printing Methylene Blue Download PDF

Info

Publication number
CN104276619B
CN104276619B CN201410529647.3A CN201410529647A CN104276619B CN 104276619 B CN104276619 B CN 104276619B CN 201410529647 A CN201410529647 A CN 201410529647A CN 104276619 B CN104276619 B CN 104276619B
Authority
CN
China
Prior art keywords
aluminium powder
dyeing
methylene blue
powder
waste water
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.)
Active
Application number
CN201410529647.3A
Other languages
Chinese (zh)
Other versions
CN104276619A (en
Inventor
徐炜
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.)
Suzhou Shengze science and Technology Pioneer Park Development Co.,Ltd.
Original Assignee
Changzhou 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 Changzhou University filed Critical Changzhou University
Priority to CN201410529647.3A priority Critical patent/CN104276619B/en
Publication of CN104276619A publication Critical patent/CN104276619A/en
Application granted granted Critical
Publication of CN104276619B publication Critical patent/CN104276619B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

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
    • C02F1/288Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
    • 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
    • B01J20/20Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/48Sorbents characterised by the starting material used for their preparation
    • B01J2220/4806Sorbents characterised by the starting material used for their preparation the starting material being of inorganic character
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/30Nature of the water, waste water, sewage or sludge to be treated from the textile industry

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Water Supply & Treatment (AREA)
  • Engineering & Computer Science (AREA)
  • Hydrology & Water Resources (AREA)
  • Inorganic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Water Treatment By Sorption (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Coloring (AREA)

Abstract

The present invention relates to a kind of method for the treatment of of dyeing and printing Methylene Blue, belong to sewage treatment area.Aluminium foil powder airslide disintegrating mill is ground into aluminium powder, and is sieved into 200-300 order; Aluminium powder after screening is placed into 1-2h in 30% ammonium peroxydisulfate, and adds 3%-5% urea wherein, at 60-70 DEG C of temperature, stir 2-3h heating, then add 10-50ppm neopelex continuation stirring 1-2h; Then vacuumize its moisture evaporate to dryness at 80-90 DEG C of temperature, be placed in 60-70 DEG C, under the protection of nitrogen, at being warming up to 800-900 DEG C, obtain modified aluminium powder adsorbent; Modified aluminium powder adsorbent and active carbon according to 1:5 mix enter into mass concentration be 5% sodium hydroxide solution soak 12-24h; Above-mentioned mixed liquor is filtered, and dry in the Muffle furnace of 100-105 DEG C, the concentration range of this raw wastewater is 620-670mg/L, is finally placed in waste water by modified aluminium powder, the concentration range of dyeing waste water Methylene Blue is 0.75-0.87mg/L after testing, and clearance is 99.87%.

Description

A kind of method for the treatment of of dyeing and printing Methylene Blue
Technical field
The present invention relates to a kind of method for the treatment of of dyeing and printing Methylene Blue, belong to sewage treatment area.
Background technology
In recent years, the product category that printing and dyeing enterprise manufactures gets more and more, and except production method difference, fibre composition also has larger change, especially in recent years the fast development of chemical fibre, so the waste water quality of discharging in its production process also usually changes.Dyeing waste water color-variable, colourity is high, enters river enter blackening in river, colourity is one of major control index of dyeing waste water, and cause the main cause of color degree of dyeing waste water to be dyestuff, they are in the transition stage of Substance Transformation, character extremely unstable, COD value is very high.According to statistics, whole world Textile Dyes to produce more than 40 ten thousand tons, more have 10%-20% dyestuff to enter waste water in dyeing and printing process process and enter water body, the dyestuff in waste water can absorb light, reduces water transparency, oxygen in a large amount of consumption water, destroy the self-purification of water, this waste water if do not processed, then can produce larger Organic to receiving water body and pollute, be that the ecosystem produces larger destruction, therefore the improvement of dyeing waste water is imperative.
Current treatment of dyeing and printing Methylene Blue many employings physico-chemical process, biological method and electrochemical method, conventional physical chemistry method has ion-exchange, ultrafiltration, membrane technology etc.; Chemical method is as Coagulation Method, oxidizing process, electrolysis etc.; Bioanalysis has anaerobic-aerobic technique etc.; find out from Some Domestic dyestuff factory waste water treatment process and effect; adopt traditional materialization, the biochemical more difficult unification reaching removal effect, financial cost, ecological protection of method dye wastewater treatment, colourity is still not easily up to standard simultaneously.And electrochemical process power consumption is large, electrode material consumption is too much, when reactant concentration is not high, the processing time extends, current efficiency ground.Therefore these methods all can not be removed well.
Summary of the invention
The present invention is directed to traditional materialization, the biochemical more difficult unification reaching removal effect, financial cost, ecological protection of method dye wastewater treatment, thus propose that a kind of removal effect is high, financial cost is low, have the method for the unified a kind for the treatment of of dyeing and printing Methylene Blue of protecting ecology.
In order to reach above-mentioned purpose, the concrete technical scheme of employing is:
1, aluminium foil powder airslide disintegrating mill is ground into aluminium powder, and utilizes standard screen screening to be 200-300 order;
2, the aluminium powder after screening is placed into 1-2h in 30% ammonium peroxydisulfate, and adds 3%-5% urea wherein, at 60-70 DEG C of temperature, stir 2-3h heating, then add 10-50ppm neopelex continuation stirring, 1-2h;
3, vacuumize its moisture evaporate to dryness at 80-90 DEG C of temperature, be placed in Muffle furnace, under the protection of nitrogen, at being warming up to 800-900 DEG C, obtain modified aluminium powder adsorbent;
4, modified aluminium powder adsorbent and active carbon according to 1:5 mix enter into mass concentration be 5% sodium hydroxide solution soak 12-24h;
5, above-mentioned mixed liquor is filtered, and dry in the Muffle furnace of 100-105 DEG C, the mixed-powder of having dried is placed in dyeing waste water, then by spectrophotometer, methylene blue in waste is detected.
Application process of the present invention is:
1, aluminium foil powder airslide disintegrating mill is ground into aluminium powder, and utilizes standard screen screening to be 200-300 order;
2, the aluminium powder after screening is placed into 1-2h in 30% ammonium peroxydisulfate, and adds 3%-5% urea wherein, at 60-70 DEG C of temperature, stir 2-3h heating, then add 10-50ppm neopelex continuation stirring, 1-2h wherein;
3, vacuumize its moisture evaporate to dryness at 80-90 DEG C of temperature, be placed in Muffle furnace, under the protection of nitrogen, at being warming up to 800-900 DEG C, obtain modified aluminium powder adsorbent;
4, modified aluminium powder adsorbent and active carbon according to 1:5 mix enter into mass concentration be 5% sodium hydroxide solution soak 12-24h;
5, above-mentioned mixed liquor is filtered, and dry in the Muffle furnace of 100-105 DEG C, the mixed-powder of having dried is placed in dyeing waste water, then by spectrophotometer, methylene blue in waste is detected.
The significant advantage that the present invention has is:
(1)with aluminium foil powder for raw material, adopt two ammonium sulfate chemical modifications, modified aluminium powder short texture, define the hole loose structure with certain adsorptivity;
(2)utilize modified aluminium powder treatment of dyeing and printing, have treatment effeciency high, not easily cause secondary pollution and the easy advantage such as control.
Specific embodiments
A method for treatment of dyeing and printing Methylene Blue, method is:
1, aluminium foil powder airslide disintegrating mill is ground into aluminium powder, and utilizes standard screen screening to be 200-300 order;
2, the aluminium powder after screening is placed into 1-2h in 30% ammonium peroxydisulfate, and adds 3%-5% urea wherein, at 60-70 DEG C of temperature, stir 2-3h heating, then add 10-50ppm neopelex continuation stirring, 1-2h wherein;
3, vacuumize its moisture evaporate to dryness at 80-90 DEG C of temperature, be placed in Muffle furnace, under the protection of nitrogen, at being warming up to 800-900 DEG C, obtain modified aluminium powder adsorbent;
4, modified aluminium powder adsorbent and active carbon according to 1:5 mix enter into mass concentration be 5% sodium hydroxide solution soak 12-24h;
5, above-mentioned mixed liquor is filtered, and dry in the Muffle furnace of 100-105 DEG C, the mixed-powder of having dried is placed in dyeing waste water, then by spectrophotometer, methylene blue in waste is detected.
Example 1
In the printing and dyeing mill in certain city, take out part dyeing waste water, detect that the concentration of this dyeing waste water Methylene Blue is 620mg/L with spectrophotometer, aluminium foil powder airslide disintegrating mill is ground into aluminium powder, and utilize standard screen screening to be 200 orders; Aluminium powder after screening is placed into 1h in 30% ammonium peroxydisulfate, and adds 3% urea wherein, at 60 DEG C of temperature, stir 2h heating, then add 25ppm neopelex continuation stirring 1h wherein; Vacuumize its moisture evaporate to dryness at 80 DEG C of temperature, be placed in Muffle furnace, under the protection of nitrogen, at being warming up to 800 DEG C, obtain modified aluminium powder adsorbent; Modified aluminium powder adsorbent and active carbon according to 1:5 mix enter into mass concentration be 5% sodium hydroxide solution soak 12h; Above-mentioned mixed liquor is filtered, and dry in the Muffle furnace of 100 DEG C, the mixed-powder of having dried is placed in dyeing waste water, then to detect to methylene blue in waste the concentration measuring methylene blue by spectrophotometer be 0.68mg/L, clearance is 99.86%, meets discharging standards.
Example 2
In the printing and dyeing mill in certain city, take out part dyeing waste water, detect that the concentration of this dyeing waste water Methylene Blue is 645mg/L with spectrophotometer, aluminium foil powder airslide disintegrating mill is ground into aluminium powder, and utilize standard screen screening to be 250 orders; Aluminium powder after screening is placed into 1.5h in 30% ammonium peroxydisulfate, and adds 4% urea wherein, at 65 DEG C of temperature, stir 2.5h heating, then add 35ppm neopelex continuation stirring 1.5h wherein; Vacuumize its moisture evaporate to dryness at 85 DEG C of temperature, be placed in Muffle furnace, under the protection of nitrogen, at being warming up to 850 DEG C, obtain modified aluminium powder adsorbent; Modified aluminium powder adsorbent and active carbon according to 1:5 mix enter into mass concentration be 5% sodium hydroxide solution soak 18h; Above-mentioned mixed liquor is filtered, and dry in the Muffle furnace of 102 DEG C, the mixed-powder of having dried is placed in dyeing waste water, then to detect to methylene blue in waste the concentration measuring methylene blue by spectrophotometer be 0.75mg/L, clearance is 99.87%, meets discharging standards.
Example 3
In the printing and dyeing mill in certain city, take out part dyeing waste water, detect that the concentration of this dyeing waste water Methylene Blue is 670mg/L with spectrophotometer, aluminium foil powder airslide disintegrating mill is ground into aluminium powder, and utilize standard screen screening to be 300 orders; Aluminium powder after screening is placed into 2h in 30% ammonium peroxydisulfate, and adds 5% urea wherein, at 70 DEG C of temperature, stir 3h heating, then add 50ppm neopelex continuation stirring 2h wherein; Vacuumize its moisture evaporate to dryness at 90 DEG C of temperature, be placed in Muffle furnace, under the protection of nitrogen, at being warming up to 900 DEG C, obtain modified aluminium powder adsorbent; Modified aluminium powder adsorbent and active carbon according to 1:5 mix enter into mass concentration be 5% sodium hydroxide solution soak 24h; Above-mentioned mixed liquor is filtered, and dry in the Muffle furnace of 105 DEG C, the mixed-powder of having dried is placed in dyeing waste water, then to detect to methylene blue in waste the concentration measuring methylene blue by spectrophotometer be 0.87mg/L, clearance is 99.87%, meets discharging standards.

Claims (1)

1. a method for treatment of dyeing and printing Methylene Blue, is characterized in that the concrete preparation process of powder of adsorbing dyeing waste water Methylene Blue is:
(1) aluminium foil powder airslide disintegrating mill is ground into aluminium powder, and utilizes standard screen screening to be 200-300 order;
(2) aluminium powder after screening being placed into mass concentration is 1-2h in the ammonium peroxydisulfate of 30%, and to add mass concentration be wherein 3%-5% urea, at 60-70 DEG C of temperature, stir 2-3h heating, then add 10-50ppm neopelex continuation stirring, 1-2h wherein;
(3) vacuumize its moisture evaporate to dryness at 80-90 DEG C of temperature, be placed in 60-70 DEG C, under the protection of nitrogen, at being warming up to 800-900 DEG C, obtain modified aluminium powder adsorbent;
(4) modified aluminium powder adsorbent is mixed according to the ratio that volume ratio is 1:5 with active carbon, enter into sodium hydroxide solution immersion 12-24h that mass concentration is 5%;
(5) above-mentioned mixed liquor is filtered, and dry in the Muffle furnace of 100-105 DEG C.
CN201410529647.3A 2014-10-09 2014-10-09 A kind of method for the treatment of of dyeing and printing Methylene Blue Active CN104276619B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410529647.3A CN104276619B (en) 2014-10-09 2014-10-09 A kind of method for the treatment of of dyeing and printing Methylene Blue

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410529647.3A CN104276619B (en) 2014-10-09 2014-10-09 A kind of method for the treatment of of dyeing and printing Methylene Blue

Publications (2)

Publication Number Publication Date
CN104276619A CN104276619A (en) 2015-01-14
CN104276619B true CN104276619B (en) 2016-03-09

Family

ID=52252036

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410529647.3A Active CN104276619B (en) 2014-10-09 2014-10-09 A kind of method for the treatment of of dyeing and printing Methylene Blue

Country Status (1)

Country Link
CN (1) CN104276619B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106219767A (en) * 2016-09-30 2016-12-14 杨新周 A kind of adsorption method of dyeing waste water Methylene Blue

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101234332A (en) * 2007-11-14 2008-08-06 北京科技大学 Method for using sewage sludge and waste graphite to prepare activated adsorption material
CN102276091A (en) * 2011-06-10 2011-12-14 南京科盛环保科技有限公司 Method for pretreating printing and dyeing wastewater with micro-electrolytic fluidized bed technique
CN102614853A (en) * 2012-03-06 2012-08-01 中国科学院广州能源研究所 Two-step preparation method for biomass material-based high-performance adsorbent

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101234332A (en) * 2007-11-14 2008-08-06 北京科技大学 Method for using sewage sludge and waste graphite to prepare activated adsorption material
CN102276091A (en) * 2011-06-10 2011-12-14 南京科盛环保科技有限公司 Method for pretreating printing and dyeing wastewater with micro-electrolytic fluidized bed technique
CN102614853A (en) * 2012-03-06 2012-08-01 中国科学院广州能源研究所 Two-step preparation method for biomass material-based high-performance adsorbent

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106219767A (en) * 2016-09-30 2016-12-14 杨新周 A kind of adsorption method of dyeing waste water Methylene Blue
CN106219767B (en) * 2016-09-30 2019-02-05 德宏师范高等专科学校 A kind of adsorption method of dyeing waste water Methylene Blue

Also Published As

Publication number Publication date
CN104276619A (en) 2015-01-14

Similar Documents

Publication Publication Date Title
US9428407B2 (en) Method for preparing anti-hardening granulous ceramic iron-carbon micro-electrolysis filler by using industrial waste
CN103241737B (en) Sludge bagasse active carbon and preparation method thereof
TWI585267B (en) Chemical pulping method
CN106753462A (en) One kind classification directional thermal decomposition sludge carbonization method
CN106432368A (en) Method of efficiently extracting fulvic acid from papermaking black liquid
CN106744789A (en) A kind of utilization lignin prepares porous charcoal and the application in ultracapacitor
CN102000545A (en) Preparation method of aluminum chloride modified bagasse active carbon
CN104276619B (en) A kind of method for the treatment of of dyeing and printing Methylene Blue
CN103466713A (en) Method for preparing manganese sulfate monohydrate with low-grade manganese ore through primary crystallization by high-pressure method
CN103131019B (en) Method extracting lignin from paper making pulp and conducting chemical modification
CN104692837A (en) Method of comprehensively utilizing sludge
CN102153266A (en) Method for treating sewage sludge with diatom
CN105540926B (en) A kind of method using acid waste water co-producing white carbon black and inorganic salts
CN101773751B (en) Lightweight cathode and anode water treatment filter material and preparation method thereof
CN105498716A (en) Waste paper fiber-based solid adsorption material and preparation method and application thereof
CN104418481A (en) Mass-energy transformation treatment process for production wastewater
Feng et al. Electro‐generation of NaOH–H2SO4 and simultaneous degradation of Acid orange 7 from Na2SO4‐containing wastewater by Ti/IrO2 electrodes
CN104276649A (en) Method for treating phenols in dyeing wastewater
CN104556621A (en) Sludge treatment method
CN104925921A (en) Method for preparing composite flocculant for printing and dyeing wastewater decolorizing treatment by using red mud
CN107974872A (en) The manufacture craft of environment-friendly paperboard
Chen et al. Removal of dye wastewater COD by sludge based activated carbon
CN105439211A (en) Energy-saving environmental-protection production method for iron oxide black pigment
CN101492234B (en) Production process for urban sewage water, sewage sludge dehydrating agent and method of use thereof
CN112537890B (en) Biochemical excess sludge reduction treatment method and treatment system

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
TR01 Transfer of patent right

Effective date of registration: 20201118

Address after: 215228, No. two, No. 1188, West Ring Road, Shengze Town, Wujiang District, Jiangsu, Suzhou

Patentee after: Suzhou Shengze science and Technology Pioneer Park Development Co.,Ltd.

Address before: Gehu Lake Road Wujin District 213164 Jiangsu city of Changzhou province No. 1

Patentee before: CHANGZHOU University

TR01 Transfer of patent right