CN104962584A - Microorganism synthesis method of Fe-containing active matter and application of Fe-containing active matter in methyl orange degradation and catalyzing field - Google Patents

Microorganism synthesis method of Fe-containing active matter and application of Fe-containing active matter in methyl orange degradation and catalyzing field Download PDF

Info

Publication number
CN104962584A
CN104962584A CN201510373800.2A CN201510373800A CN104962584A CN 104962584 A CN104962584 A CN 104962584A CN 201510373800 A CN201510373800 A CN 201510373800A CN 104962584 A CN104962584 A CN 104962584A
Authority
CN
China
Prior art keywords
tropeolin
containing active
active matter
catalyzer
methyl orange
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
CN201510373800.2A
Other languages
Chinese (zh)
Inventor
张莹
王敏
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to CN201510373800.2A priority Critical patent/CN104962584A/en
Publication of CN104962584A publication Critical patent/CN104962584A/en
Pending legal-status Critical Current

Links

Abstract

The invention relates to a matter microorganism synthesis method of Fe-containing active matter and application of the Fe-containing active matter in the methyl orange degradation and catalyzing field. By means of the method, the Fe-containing active matter is prepared easily, other raw materials are cheap and easy to obtain, the method that Fe-containing containing matter is degraded through a catalyst is simple and efficient, the Fe-containing active matter can generate Fe(OH)2+, Fe(OH)2+ and Fe2(OH)24+ which are high in activity in water, and these substances are in cooperation with titanium dioxide under the action of organic acid and oxygen to generate oxygen radicals with the high oxidizing property, so that the methyl orange can be degraded thoroughly, the degradation effect is remarkable, and the method is suitable for treating sewage containing the methyl orange on a large scale.

Description

A kind of Microbe synthesis method of iron content actives and the application at methyl orange degradation catalytic field thereof
Technical field
The present invention relates to a kind of catalyzer, particularly relate to a kind of Microbe synthesis method of iron content actives and the application at methyl orange degradation catalytic field thereof, belong to dye degrades field.
Background technology
Dyestuff to make filamentary material or other materials obtain the distinct and organism of solid color, and dye soluble, in water solvent, maybe can be transformed into solution and dye, or is processed into dispersion state and is employed, and it is mainly used in the dyeing of textiles and leather.Its history is almost long equally with human history, the dyestuff of early application is all natural, and within 1856, Englishize scholar Perkin synthesizes first synthetic dyestuff mauvein (e), 20 beginnings of the century, synthetic dyestuff almost instead of natural dyestuff completely, current commercial dye oneself have kind more than 10,000.
The sorting technique of dyestuff has two kinds, and one is classify according to the chemical structure of dyestuff, and two is classify according to the application method of dyestuff, and be with basic structure similar in dye molecule for foundation, dyestuff can be divided into azoic dyestuff, anthraquinone dye and indigoids dyestuff etc.; By the tint applications property sort of dyestuff, dyestuff can be divided into matching stain, basic dyestuff and neutral dye etc.Along with the development of dyestuffs industries, the problem of environmental pollution becomes increasingly conspicuous, and a large amount of waste water how processing dyestuffs industries generation become the emphasis of people's research.
In the molecular structure of dyestuff, all have conjugated system, the dyestuff wherein containing azo-group (-N=N-) is called azoic dyestuff.Now, commercial dye more than half is containing azo-group, and the dyestuff that textile industry uses about 70% is azoic dyestuff, the azoic dyestuff that nearly 2000 various structures are different.Tropeolin-D, the one of azoic dyestuff, formal name used at school is to dimethylaminoazobenzene sodium sulfonate, and it is the acetate by p-aminophenyl sulphur diazonium salt and-DMA, in weak acid medium, coupling obtains, what coupling first obtained is red acidic methylene orange, and be called turmeric yellow, in alkalescence, turmeric yellow changes the sodium salt of tropeolin-D into, i.e. tropeolin-D (Methyl Orange, MO).Tropeolin-D is reagent conventional in chemical experiment, and the methyl orange aqueous solution of 0.1% is conventional acid base indicator, pH value color change interval 3.1 (red)-4.4 (Huang).
In the last few years, about the carinogenicity of aromatic amine azoic dyestuff receives much concern.Because some dyestuff may be transferred to the skin of people from textiles, when particularly dyefastness is not good, under the biocatalysis of bacterium, may reduction reaction be there is in the dyestuff that skin has been stained with, and discharge multiple carcinogenic aromatic amine, these carcinogenss in human body, become the risk factor of human lesion through skin diffusion, thus bring out cancer or cause allergy.
After undressed waste water from dyestuff directly discharges entered environment water body, on the one hand because dyestuff affects the transmission of light, thus affect the photosynthesis of waterplant, finally cause waterplant dead, and then cause interruption and the water hypoxia of food chain in water body, make whole water ecosystem close to collapse; On the other hand dyestuff especially azo dyes belong to and three to cause the hazardous and noxious substances of (carcinogenic, teratogenesis, mutagenesis), there is direct killing effect to the animal in water body, enter after human body can cause the malignant diseases such as human malignancies through food chain enrichment.
Coagulant sedimentation, absorption method, By Bubble-floating Method, biological process and chemical oxidization method etc. are had at present for the method containing Methyl Orange in Wastewater process.The shortcoming that these methods exist is: removal effect is not thorough, higher to environmental requirement, synthesis technique is more complicated, therefore needs the Water Pollution Problem that the process of a kind of cost-effective dye discoloration recovery technique is day by day serious badly.
Summary of the invention
The present invention is directed to the deficiency that above-mentioned prior art exists, a kind of Microbe synthesis method of iron content actives and the application at methyl orange degradation catalytic field thereof are provided.
The technical scheme that the present invention solves the problems of the technologies described above is as follows: a kind of Microbe synthesis method of iron content actives, and step is as follows:
(1) in reactor, add FeSO4 〃 7H2O and iron protoxide bacillus Acidithtobacillusferrooxidans LX5 suspension thalline, the pH regulating reaction solution with dilute sulphuric acid is 1.5 ~ 3.0;
(2) mixed solution of step (1) is placed in 28 DEG C of reciprocal shaker shaking culture 1 ~ 3 day;
(3) mixed solution after step (2) being cultivated filters, and the pH of gained throw out sulfuric acid acidation is the distilled water wash 2 ~ 3 times of 1.5 ~ 2.5, then uses distilled water wash 2 ~ 3 times, dries to obtain product.
Second object of the present invention is to provide a kind of catalyzer for tropeolin-D in degradation of sewage, comprise iron content actives, organic acid and titanium dioxide described above, its component by weight mark is counted: iron content actives 73 ~ 76%, organic acid 18 ~ 20% and titanium dioxide 5 ~ 7%.
Wherein, described organic acid is citric acid, tartrate, oxalic acid or EDTA.
3rd object of the present invention is a kind of method providing catalyzer described above for tropeolin-D of degrading, and step is as follows:
(1) get above-mentioned catalyzer 1g to add in the beaker of 1000g containing the waste water of tropeolin-D, fully mix;
(2) under the waste water mixed being placed in room temperature, Keep agitation 2h;
(3) its absorbancy is surveyed at tropeolin-D maximum absorption wavelength 463nm place, the residual content of tropeolin-D in wastewater measurement.
The invention has the beneficial effects as follows: iron content actives preparation of the present invention is simple, and other cheaper starting materials are easy to get, and catalyzer is simply efficient to the degradation method of tropeolin-D, and iron content active substance can produce active higher Fe (OH) in water 2+, Fe (OH) 2+and Fe 2(OH) 2 4+, these materials work in coordination with titanium dioxide the oxygen radical producing and have strong oxidizing property under organic acid, oxygen effect, thus degraded thoroughly, and Be very effective is applicable to process large-scale containing tropeolin-D sewage.
Embodiment
Be described principle of the present invention and feature below in conjunction with example, example, only for explaining the present invention, is not intended to limit scope of the present invention.
The instrument that the embodiment of the present invention uses is T-6 series ultraviolet-visible spectrophotometer (Beijing Pu Xi general instrument Corp.).
Embodiment 1
For a catalyzer for tropeolin-D in degradation of sewage, its component by weight mark is counted: iron content actives 73%, citric acid 20% and titanium dioxide 7%.
Wherein, the Microbe synthesis method of iron content actives, step is as follows:
(1) in reactor, add FeSO4 〃 7H2O and iron protoxide bacillus Acidithtobacillusferrooxidans LX5 suspension thalline, the pH regulating reaction solution with dilute sulphuric acid is 1.5;
(2) mixed solution of step (1) is placed in 28 DEG C of reciprocal shaker shaking culture 1 day;
(3) mixed solution after step (2) being cultivated filters, and the pH of gained throw out sulfuric acid acidation is the distilled water wash 2 times of 1.5, then uses distilled water wash 2 times, dries to obtain product.
Catalyzer described above is for the method for tropeolin-D of degrading, and step is as follows:
(1) get above-mentioned catalyzer 1g to add in the beaker of 1000g containing the waste water of tropeolin-D, fully mix;
(2) under the waste water mixed being placed in room temperature, Keep agitation 2h;
(3) survey its absorbancy at tropeolin-D maximum absorption wavelength 463nm place, in wastewater measurement, the residual content of tropeolin-D, the results are shown in Table 1.
Embodiment 2
For a catalyzer for tropeolin-D in degradation of sewage, its component by weight mark is counted: iron content actives 76%, tartrate 18% and titanium dioxide 6%.
Wherein, the Microbe synthesis method of iron content actives, step is as follows:
(1) in reactor, add FeSO4 〃 7H2O and iron protoxide bacillus Acidithtobacillusferrooxidans LX5 suspension thalline, the pH regulating reaction solution with dilute sulphuric acid is 3.0;
(2) mixed solution of step (1) is placed in 28 DEG C of reciprocal shaker shaking culture 3 days;
(3) mixed solution after step (2) being cultivated filters, and the pH of gained throw out sulfuric acid acidation is the distilled water wash 3 times of 2.5, then uses distilled water wash 3 times, dries to obtain product.
Catalyzer described above is for the method for tropeolin-D of degrading, and step is as follows:
(1) get above-mentioned catalyzer 1g to add in the beaker of 1000g containing the waste water of tropeolin-D, fully mix;
(2) under the waste water mixed being placed in room temperature, Keep agitation 2h;
(3) survey its absorbancy at tropeolin-D maximum absorption wavelength 463nm place, in wastewater measurement, the residual content of tropeolin-D, the results are shown in Table 1.
Embodiment 3
For a catalyzer for tropeolin-D in degradation of sewage, its component by weight mark is counted: iron content actives 76%, oxalic acid 19% and titanium dioxide 5%.
Wherein, the Microbe synthesis method of iron content actives, step is as follows:
(1) in reactor, add FeSO4 〃 7H2O and iron protoxide bacillus Acidithtobacillusferrooxidans LX5 suspension thalline, the pH regulating reaction solution with dilute sulphuric acid is 2.0;
(2) mixed solution of step (1) is placed in 28 DEG C of reciprocal shaker shaking culture 2 days;
(3) mixed solution after step (2) being cultivated filters, and the pH of gained throw out sulfuric acid acidation is the distilled water wash 3 times of 2.0, then uses distilled water wash 3 times, dries to obtain product.
Catalyzer described above is for the method for tropeolin-D of degrading, and step is as follows:
(1) get above-mentioned catalyzer 1g to add in the beaker of 1000g containing the waste water of tropeolin-D, fully mix;
(2) under the waste water mixed being placed in room temperature, Keep agitation 2h;
(3) survey its absorbancy at tropeolin-D maximum absorption wavelength 463nm place, in wastewater measurement, the residual content of tropeolin-D, the results are shown in Table 1.
Table 1
As can be seen from Table 1, iron content actives prepared by the present invention and organic acid, titanium dioxide are in conjunction with the catalyzer of gained, very remarkable for the degradation effect containing tropeolin-D sewage, and action time is short.
The foregoing is only preferred embodiment of the present invention, not in order to limit the present invention, within the spirit and principles in the present invention all, any amendment done, equivalent replacement, improvement etc., all should be included within protection scope of the present invention.

Claims (4)

1. a Microbe synthesis method for iron content actives, it is characterized in that, step is as follows:
(1) in reactor, add FeSO47H2O and iron protoxide bacillus Acidithtobacillusferrooxidans LX5 suspension thalline, the pH regulating reaction solution with dilute sulphuric acid is 1.5 ~ 3.0;
(2) mixed solution of step (1) is placed in 28 DEG C of reciprocal shaker shaking culture 1 ~ 3 day;
(3) mixed solution after step (2) being cultivated filters, and the pH of gained throw out sulfuric acid acidation is the distilled water wash 2 ~ 3 times of 1.5 ~ 2.5, then uses distilled water wash 2 ~ 3 times, dries to obtain product.
2. for a catalyzer for tropeolin-D in degradation of sewage, it is characterized in that, its component by weight mark is counted: iron content actives 73 ~ 76%, organic acid 18 ~ 20% and titanium dioxide 5 ~ 7%.
3. catalyzer according to claim 2, is characterized in that, described organic acid is citric acid, tartrate, oxalic acid or EDTA.
4. catalyzer according to claim 2 is for a method for tropeolin-D of degrading, it is characterized in that, step is as follows:
(1) get catalyzer 1g to add in the beaker of 1000g containing the waste water of tropeolin-D, fully mix;
(2) under the waste water mixed being placed in room temperature, Keep agitation 2h;
(3) its absorbancy is surveyed at tropeolin-D maximum absorption wavelength 463nm place, the residual content of tropeolin-D in wastewater measurement.
CN201510373800.2A 2015-06-30 2015-06-30 Microorganism synthesis method of Fe-containing active matter and application of Fe-containing active matter in methyl orange degradation and catalyzing field Pending CN104962584A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510373800.2A CN104962584A (en) 2015-06-30 2015-06-30 Microorganism synthesis method of Fe-containing active matter and application of Fe-containing active matter in methyl orange degradation and catalyzing field

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510373800.2A CN104962584A (en) 2015-06-30 2015-06-30 Microorganism synthesis method of Fe-containing active matter and application of Fe-containing active matter in methyl orange degradation and catalyzing field

Publications (1)

Publication Number Publication Date
CN104962584A true CN104962584A (en) 2015-10-07

Family

ID=54216672

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510373800.2A Pending CN104962584A (en) 2015-06-30 2015-06-30 Microorganism synthesis method of Fe-containing active matter and application of Fe-containing active matter in methyl orange degradation and catalyzing field

Country Status (1)

Country Link
CN (1) CN104962584A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110787626A (en) * 2019-11-19 2020-02-14 四川大学 Method for low-temperature plasma coupling photocatalytic oxidation of nitrogen oxide
CN111389401A (en) * 2020-03-27 2020-07-10 北京化工大学 For the efficient catalytic conversion of CO2Preparation method of microorganism coupling catalytic system

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1692977A (en) * 2005-03-17 2005-11-09 华中科技大学 Compound photocatalyst using titanium dioxide as its base, and its prepn. method
CN102372355A (en) * 2011-10-09 2012-03-14 广东省生态环境与土壤研究所 Method for processing organic waste water
CN103877927A (en) * 2014-04-14 2014-06-25 南华大学 Preparation method of magnetic nano Fe3O4 particles by biological catalysis and application of particles to treatment of uranium-containing wastewater

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1692977A (en) * 2005-03-17 2005-11-09 华中科技大学 Compound photocatalyst using titanium dioxide as its base, and its prepn. method
CN102372355A (en) * 2011-10-09 2012-03-14 广东省生态环境与土壤研究所 Method for processing organic waste water
CN103877927A (en) * 2014-04-14 2014-06-25 南华大学 Preparation method of magnetic nano Fe3O4 particles by biological catalysis and application of particles to treatment of uranium-containing wastewater

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
刘宗耀等: "纳米Fe2O3-TiO2催化剂的制备及其对甲基橙的降解", 《化工环保》 *
深圳市长隆科技有限公司: ""硫酸铁水解产生什么化学物质"", 《WWW.C139.COM/NEWS/1592.SHTML》 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110787626A (en) * 2019-11-19 2020-02-14 四川大学 Method for low-temperature plasma coupling photocatalytic oxidation of nitrogen oxide
CN111389401A (en) * 2020-03-27 2020-07-10 北京化工大学 For the efficient catalytic conversion of CO2Preparation method of microorganism coupling catalytic system
CN111389401B (en) * 2020-03-27 2021-07-23 北京化工大学 For the efficient catalytic conversion of CO2Preparation method of microorganism coupling catalytic system

Similar Documents

Publication Publication Date Title
Alsukaibi Various approaches for the detoxification of toxic dyes in wastewater
Shindhal et al. A critical review on advances in the practices and perspectives for the treatment of dye industry wastewater
Nachiyar et al. Developments in treatment technologies of dye-containing effluent: A review
Maheshwari et al. Dye pollution in water and wastewater
Roy et al. Dyes and their removal technologies from wastewater: A critical review
Mani et al. Textile industry wastewater: environmental and health hazards and treatment approaches
Shah Biodegradation of azo dye compounds
Koprivanac et al. Influence of iron on degradation of organic dyes in corona
Depraetere et al. Decolorisation of piggery wastewater to stimulate the production of Arthrospira platensis
Hasegawa et al. COD removal and toxicity decrease from tannery wastewater by zinc oxide-assisted photocatalysis: a case study
Punzi Treatment of textile wastewater by combining biological processes and advanced oxidation
Masalvad et al. Application of photo Fenton process for treatment of textile Congo-red dye solution
Shah Bioremediation of azo dye
Rane et al. Biodecolorization and biodegradation of dyes: A review
Singh et al. Present status of biodegradation of textile dyes
Amritha et al. Degradation of nitroaromatic compounds: a novel approach using iron from laterite soil
CN104962584A (en) Microorganism synthesis method of Fe-containing active matter and application of Fe-containing active matter in methyl orange degradation and catalyzing field
El-Sikaily et al. Textile dyes xenobiotic and their harmful effect
CN103420475A (en) Method for treating organic wastewater containing aniline through Fenton catalytic degradation reaction
Sahoo et al. Biological methods for textile dyes removal from wastewaters
CN108455757A (en) A kind of processing method of amino benzene analog waste water
Fatimah et al. The use of artificial neural network for modeling the decolourization of acid orange 7 solution of industrial by ozonation process
Eslami et al. Removal of reactive dyes from textile wastewater using sonochemical process: effective parameters study
Vaish et al. Bionano technological approaches for degradation and decolorization of dye by mangrove plants
Øllgaard et al. Survey of azo-colorants in Denmark

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20151007

RJ01 Rejection of invention patent application after publication