CN107661750A - A kind of preparation method of waste water from dyestuff compounding adsorbent - Google Patents
A kind of preparation method of waste water from dyestuff compounding adsorbent Download PDFInfo
- Publication number
- CN107661750A CN107661750A CN201711052299.5A CN201711052299A CN107661750A CN 107661750 A CN107661750 A CN 107661750A CN 201711052299 A CN201711052299 A CN 201711052299A CN 107661750 A CN107661750 A CN 107661750A
- Authority
- CN
- China
- Prior art keywords
- preparation
- waste water
- chitosan
- activated carbon
- 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
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/20—Solid 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
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/24—Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/288—Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/308—Dyes; Colorants; Fluorescent agents
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Analytical Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Inorganic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Water Treatment By Sorption (AREA)
Abstract
The invention discloses a kind of preparation method of waste water from dyestuff compounding adsorbent, comprise the following steps:By chitosan and activated carbon it is uniform mix after add glacial acetic acid, glutaraldehyde is added after stirring swelling a period of time, and crosslinking is stirred in water bath with thermostatic control, then washed with sodium hydroxide solution, remaining glutaraldehyde is removed, washs, dries, mills, sieving finally obtained required cross-linking type chitosan/activated carbon;Wherein, chitosan, activated carbon, glacial acetic acid three mass ratio are 8~6 in the preparation method:3~2:1.Preparation method technique of the present invention is simple, obtained chitosan/activated carbon compounding adsorbent, adsorption treatment is carried out to waste water from dyestuff by the way of physics and chemisorbed are combined, adsorption effect is notable, effectively raise the clearance of waste water, secondary pollution will not be produced after processing, is had a good application prospect.
Description
Technical field
The invention belongs to technical field of waste water processing, and in particular to a kind of preparation method of waste water from dyestuff compounding adsorbent.
Background technology
In recent years, the improvement of waste water from dyestuff has become one of study hotspot of water treatment field.In early days, conventional dyestuff
Method of wastewater treatment mainly says solution including flocculent precipitation, chemical oxidization method, membrane separation process and biology.Although these methods can
To reduce the content of dyestuff in waste water from dyestuff to a certain extent, but still there is it is of all kinds the defects of, for example, because of absorption
Rate is low, processing cost is too high and the bad adaptability to waste water from dyestuff composition transfer, result be it is not good enough to the removal effect of dyestuff, separately
It is also possible to that poisonous and harmful accessory substance or a large amount of sludge can be produced in external processing procedure, so as to cause secondary pollution.
The content of the invention
It is an object of the invention to provide a kind of adsorption effect significantly and will not produce secondary pollution waste water from dyestuff compounding
The preparation method of adsorbent.
The technical solution for realizing the object of the invention is:
A kind of preparation method of waste water from dyestuff compounding adsorbent, comprises the following steps:By the uniform of chitosan and activated carbon
Glacial acetic acid is added after mixing, add glutaraldehyde after stirring swelling a period of time is stirred crosslinking in water bath with thermostatic control, then uses
Sodium hydroxide solution is washed, and removes remaining glutaraldehyde, is washed, is dried, mills, sieving finally obtained required cross-linking type
Chitosan/activated carbon;Wherein, chitosan, activated carbon, glacial acetic acid three mass ratio are 8~6 in the preparation method:3~2:1.
The concentration of the sodium hydroxide is 25-35mg/L.
The concentration of glutaraldehyde described in the preparation method is 5-30mg/L.
The mixing time is 2-3h.
The bath temperature is 40-50 DEG C.
Compared with prior art, its remarkable advantage is the present invention:
Preparation method technique of the present invention is simple, obtained chitosan/activated carbon compounding adsorbent, is inhaled using physics and chemistry
The attached mode being combined carries out adsorption treatment to waste water from dyestuff, and adsorption effect is notable, effectively raises the clearance of waste water, place
Secondary pollution will not be produced after reason, is had a good application prospect.
Embodiment
The present invention is described in further detail with reference to specific embodiment.
Embodiment 1
A kind of preparation method of waste water from dyestuff compounding adsorbent, comprises the following steps:By the uniform of chitosan and activated carbon
Glacial acetic acid is added after mixing, add glutaraldehyde after stirring swelling a period of time is stirred crosslinking in water bath with thermostatic control, then uses
Sodium hydroxide solution is washed, and removes remaining glutaraldehyde, is washed, is dried, mills, sieving finally obtained required cross-linking type
Chitosan/activated carbon;Wherein, chitosan, activated carbon, glacial acetic acid three mass ratio are 8 in the preparation method:3:1;The hydrogen
The concentration of sodium oxide molybdena is 25mg/L;The concentration of glutaraldehyde described in the preparation method is 5mg/L;The mixing time is 3h;
The bath temperature is 40 DEG C.
Embodiment 2
A kind of preparation method of waste water from dyestuff compounding adsorbent, comprises the following steps:By the uniform of chitosan and activated carbon
Glacial acetic acid is added after mixing, add glutaraldehyde after stirring swelling a period of time is stirred crosslinking in water bath with thermostatic control, then uses
Sodium hydroxide solution is washed, and removes remaining glutaraldehyde, is washed, is dried, mills, sieving finally obtained required cross-linking type
Chitosan/activated carbon;Wherein, chitosan, activated carbon, glacial acetic acid three mass ratio are 6 in the preparation method:2:1;The hydrogen
The concentration of sodium oxide molybdena is 35mg/L;The concentration of glutaraldehyde described in the preparation method is 30mg/L;The mixing time is 2h;
The bath temperature is 50 DEG C.
Embodiment 3
A kind of preparation method of waste water from dyestuff compounding adsorbent, comprises the following steps:By the uniform of chitosan and activated carbon
Glacial acetic acid is added after mixing, add glutaraldehyde after stirring swelling a period of time is stirred crosslinking in water bath with thermostatic control, then uses
Sodium hydroxide solution is washed, and removes remaining glutaraldehyde, is washed, is dried, mills, sieving finally obtained required cross-linking type
Chitosan/activated carbon;Wherein, chitosan, activated carbon, glacial acetic acid three mass ratio are 8 in the preparation method:3:1;The hydrogen
The concentration of sodium oxide molybdena is 25mg/L;The concentration of glutaraldehyde described in the preparation method is 20mg/L;The mixing time is 3h;
The bath temperature is 50 DEG C.
Embodiment 4
A kind of preparation method of waste water from dyestuff compounding adsorbent, comprises the following steps:By the uniform of chitosan and activated carbon
Glacial acetic acid is added after mixing, add glutaraldehyde after stirring swelling a period of time is stirred crosslinking in water bath with thermostatic control, then uses
Sodium hydroxide solution is washed, and removes remaining glutaraldehyde, is washed, is dried, mills, sieving finally obtained required cross-linking type
Chitosan/activated carbon;Wherein, chitosan, activated carbon, glacial acetic acid three mass ratio are 7 in the preparation method:3:1;The hydrogen
The concentration of sodium oxide molybdena is 30mg/L;The concentration of glutaraldehyde described in the preparation method is 25mg/L;The mixing time is 2h;
The bath temperature is 45 DEG C.
Embodiment 5
A kind of preparation method of waste water from dyestuff compounding adsorbent, comprises the following steps:By the uniform of chitosan and activated carbon
Glacial acetic acid is added after mixing, add glutaraldehyde after stirring swelling a period of time is stirred crosslinking in water bath with thermostatic control, then uses
Sodium hydroxide solution is washed, and removes remaining glutaraldehyde, is washed, is dried, mills, sieving finally obtained required cross-linking type
Chitosan/activated carbon;Wherein, chitosan, activated carbon, glacial acetic acid three mass ratio are 6 in the preparation method:3:1;The hydrogen
The concentration of sodium oxide molybdena is 33mg/L;The concentration of glutaraldehyde described in the preparation method is 8mg/L;The mixing time is 2h;
The bath temperature is 48 DEG C.
Claims (5)
1. a kind of preparation method of waste water from dyestuff compounding adsorbent, it is characterised in that comprise the following steps:By chitosan and activity
Glacial acetic acid is added after the uniform mixing of charcoal, add glutaraldehyde after stirring swelling a period of time is stirred friendship in water bath with thermostatic control
Connection, is then washed with sodium hydroxide solution, removes remaining glutaraldehyde, is washed, is dried, mills, sieving finally obtained institute
Cross-linking type chitosan/the activated carbon needed;Wherein, chitosan, activated carbon, glacial acetic acid three mass ratio are 8 in the preparation method
~6:3~2:1.
A kind of 2. preparation method of waste water from dyestuff compounding adsorbent according to claim 1, it is characterised in that the hydrogen-oxygen
The concentration for changing sodium is 25-35mg/L.
A kind of 3. preparation method of waste water from dyestuff compounding adsorbent according to claim 1, it is characterised in that the preparation
The concentration of glutaraldehyde described in method is 5-30mg/L.
A kind of 4. preparation method of waste water from dyestuff compounding adsorbent according to claim 1, it is characterised in that the stirring
Time is 2-3h.
A kind of 5. preparation method of waste water from dyestuff compounding adsorbent according to claim 1, it is characterised in that the water-bath
Temperature is 40-50 DEG C.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201711052299.5A CN107661750A (en) | 2017-10-30 | 2017-10-30 | A kind of preparation method of waste water from dyestuff compounding adsorbent |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201711052299.5A CN107661750A (en) | 2017-10-30 | 2017-10-30 | A kind of preparation method of waste water from dyestuff compounding adsorbent |
Publications (1)
Publication Number | Publication Date |
---|---|
CN107661750A true CN107661750A (en) | 2018-02-06 |
Family
ID=61143814
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201711052299.5A Pending CN107661750A (en) | 2017-10-30 | 2017-10-30 | A kind of preparation method of waste water from dyestuff compounding adsorbent |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN107661750A (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109046268A (en) * | 2018-08-28 | 2018-12-21 | 武汉霖泉环保科技有限公司 | A kind of sewage treatment multifunctional ceiling enclosure material and preparation method thereof |
CN109735134A (en) * | 2018-12-11 | 2019-05-10 | 佛山市名洲纺织有限公司 | A kind of dye powder and preparation method thereof that keratin base is bamboo charcoal modified |
CN112206748A (en) * | 2019-07-10 | 2021-01-12 | 中国石化扬子石油化工有限公司 | Preparation method of efficient composite adsorbent for refining pentadecanedioic acid |
CN112516961A (en) * | 2020-11-09 | 2021-03-19 | 江西佳霖炭业科技有限公司 | Preparation method of coconut shell activated carbon with antibacterial function |
-
2017
- 2017-10-30 CN CN201711052299.5A patent/CN107661750A/en active Pending
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109046268A (en) * | 2018-08-28 | 2018-12-21 | 武汉霖泉环保科技有限公司 | A kind of sewage treatment multifunctional ceiling enclosure material and preparation method thereof |
CN109046268B (en) * | 2018-08-28 | 2022-02-11 | 武汉霖泉环保科技有限公司 | Multifunctional adsorption material for sewage treatment and preparation method thereof |
CN109735134A (en) * | 2018-12-11 | 2019-05-10 | 佛山市名洲纺织有限公司 | A kind of dye powder and preparation method thereof that keratin base is bamboo charcoal modified |
CN112206748A (en) * | 2019-07-10 | 2021-01-12 | 中国石化扬子石油化工有限公司 | Preparation method of efficient composite adsorbent for refining pentadecanedioic acid |
CN112516961A (en) * | 2020-11-09 | 2021-03-19 | 江西佳霖炭业科技有限公司 | Preparation method of coconut shell activated carbon with antibacterial function |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN107661750A (en) | A kind of preparation method of waste water from dyestuff compounding adsorbent | |
CN107188293B (en) | Method for degrading organic pollutants by using manganese-zinc ferrite activated persulfate prepared from waste batteries | |
CN104671627A (en) | Method for promoting anaerobic degradation of estrogen NP (nonyl phenol) in sludge under combined action of surfactant and alkali treatment | |
CN110885108B (en) | Efficient harmless treatment method for mine copper cyanide wastewater | |
CN107552014A (en) | A kind of Universal Dye waste water treating agent | |
CN104609652A (en) | Coupling processing technology for steadily improving biodegradability of coking wastewater | |
CN107055892B (en) | Method for microwave-assisted catalytic oxidation of biochemical tail water of brewing wastewater by compounding of multiple metals | |
CN103708596B (en) | In a kind of white wine wastewater conventional process, strengthening is removed and reclaims the method for nitrogen phosphorus | |
CN104724896A (en) | Method for promoting anaerobic degradation of estrogen nonylphenol in sludge through alkali treatment | |
CN107572641A (en) | A kind of preparation method of built-up flocculant | |
CN107056124B (en) | A kind of preparation method of cement grinding aid | |
CN100572296C (en) | A kind of method of yeast wastewater advanced treatment | |
CN108083450B (en) | Complexing agent for rare earth wastewater | |
CN102616924B (en) | Method for increasing biochemical treatment ability of printing and dyeing wastewater by utilizing enzyme activity soybean meal | |
CN112961124B (en) | Method for treating sewage by using microbial preparation | |
CN107758877B (en) | Industrial sewage treating agent and preparation method thereof | |
CN104211106A (en) | Preparation method of rare earth carbonate free of generation of ammonia-nitrogen wastewater | |
CN104651341A (en) | Method for performing bio-enzyme immobilization through rice bran | |
CN105174527B (en) | Method for carrying out selective oxidation treatment on beneficiation wastewater | |
CN203440203U (en) | Sewage treatment device | |
CN107311330B (en) | Method for decoloring alcohol biochemical tail water | |
CN109775919B (en) | Biochemical environment-friendly process for effectively treating xanthan gum industrial wastewater | |
CN104310645A (en) | Method for treating papermaking wastewater by using modified fly ash | |
CN105061191B (en) | A kind of method that diene alcohol ketone acetic ester waste acid water recycles | |
CN107473444B (en) | Method for recovering nitrogen and phosphorus nutrient elements from pig farm tail water |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
WD01 | Invention patent application deemed withdrawn after publication | ||
WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20180206 |