CN108298661A - The method that produced exhaust-gas efficient removes methylene blue is pre-processed using jerusalem artichoke core - Google Patents
The method that produced exhaust-gas efficient removes methylene blue is pre-processed using jerusalem artichoke core Download PDFInfo
- Publication number
- CN108298661A CN108298661A CN201810096865.0A CN201810096865A CN108298661A CN 108298661 A CN108298661 A CN 108298661A CN 201810096865 A CN201810096865 A CN 201810096865A CN 108298661 A CN108298661 A CN 108298661A
- Authority
- CN
- China
- Prior art keywords
- core
- jerusalem artichoke
- methylene blue
- reaction
- method described
- 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.)
- Granted
Links
Classifications
-
- 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
- C02F1/58—Treatment of water, waste water, or sewage by removing specified dissolved compounds
-
- 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
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/30—Nature of the water, waste water, sewage or sludge to be treated from the textile industry
Abstract
The method that produced exhaust-gas efficient removes methylene blue is pre-processed using jerusalem artichoke core the present invention provides a kind of comprising following steps:It collects jerusalem artichoke core and pre-processes produced exhaust gas, be passed through equipped in the closed container in methylene blue waste liquid, degradation reaction is carried out in 30~80 DEG C;The pretreated method of jerusalem artichoke core is:Jerusalem artichoke core is put into reaction kettle, concentrated phosphoric acid hydrogen peroxide mix reagent is added and carries out pretreatment reaction, wherein the mass fraction of concentrated phosphoric acid is 60.0~70.0%, and the mass fraction of hydrogen peroxide is 5.0~8.0%.The present invention has outstanding removal effect for common methylene blue, avoid existing the drawbacks of base and liquid-based treatment technology need to carry out special modification to raw material admittedly, truly realize " with it is useless directly control it is useless " technical purpose, realize bio-ethanol and prepare and the combination of two industries of wastewater treatment.
Description
Technical field
The invention belongs to technical field of waste water processing, and in particular to a kind of to be gone using the produced exhaust-gas efficient of jerusalem artichoke core pretreatment
Except the method for methylene blue.
Background technology
China is traditional textile big country, and in recent years, with the proposition required structural transformation of the economy, textile fabric production is discarded
The improvement of object treatment technology will increasingly be taken seriously.Dyestuff is one of main pollutant in textile fabric production process,
Complicated component has bio-toxicity and refractory organics more, is a kind of waste water difficult to deal with.
At this stage, it is absorption method, membrane separation process, Ozonation and photocatalytic method to the conventional method of the processing of pollution.
Authorization Notice No. provides a kind of processing method of waste water from dyestuff for the Chinese patent of 102659235 B of CN, passes through
The mode of multiphase Fenton catalysis oxidations solves the deficiency of common homogeneous Fenton oxidation, has significantly increased for organic waste
The efficiency of water process.
Authorization Notice No. provides a kind of method of processing waste water from dyestuff for the Chinese patent of 103588307 B of CN, utilizes
Microorganism electrochemical coupled system realizes the promotion to the degradation efficiency of waste water from dyestuff, is gone to acid orange 7 and methyl orange
Except efficiency respectively reaches 79% and 89.8%.
Authorization Notice No. provides the ecology of a kind of dyestuff or dyestuff intermediate for the Chinese patent of 104725897 B of CN
Environment-friendly treatment method, by the way that water, alkaline agent and organic solvent are added in azo dyes or aromatic amine dyestuff, after heating reaction,
It can get higher removal effect.
Authorization Notice No. provides a kind of microwave of waste water from dyestuff for the Chinese patent of 103739035 B of CN and quickly handles
Method realizes the promotion to the degradation treatment efficiency of dyestuff using the technology of nano zero valence iron combination microwave treatment.
Authorization Notice No. provides for China of 104310559 B of CN and a kind of handling waste water from dyestuff using modified straw
Method, utilize absorption of the modified straw to dyestuff, realize to orange II, eriochrome black T decoloring dye waste water rate reach 95% with
On, 75% or more removal effect is reached to methylene blue dye wastewater percent of decolourization.
By above to the illustration of the treatment technology of existing waste water from dyestuff it is found that at present for the place of waste water from dyestuff
Reason, is typically based on solid absorbent or liquid reactions reagent carries out.Although the prior art realize to a certain extent " with
It is useless control it is useless ", by being modified processing to some industrial and agricultural production wastes, the product of removing dyestuff can be obtained, but this
The cost of a little modifications is usually higher, and the value of popularization and application is relatively low.Therefore, develop it is a kind of with existing production activity generate
Direct waste carry out " with it is useless directly control it is useless " handle dyestuff, be the project of next stage primary study.
Invention content
In view of the shortcomings of the prior art, the purpose of the present invention is to provide a kind of produced exhaust gas height is pre-processed using jerusalem artichoke core
The method of effect removal methylene blue, described method includes following steps:
It collects jerusalem artichoke core and pre-processes produced exhaust gas, be passed through equipped in the closed container in methylene blue waste liquid, in 30~80
Degradation reaction is carried out in DEG C;
The pretreated method of jerusalem artichoke core is:
Jerusalem artichoke core is put into reaction kettle, concentrated phosphoric acid-hydrogen peroxide mix reagent is added and carries out pretreatment reaction, wherein
The mass fraction of concentrated phosphoric acid is 60.0~70.0%, and the mass fraction of hydrogen peroxide is 5.0~8.0%.
The present inventor has carried out combining hydrogen peroxide using concentrated phosphoric acid in grant number is 103555774 B of CN
Preprocessing lignocellulose class raw material is used for the research of enzyme hydrolysis, and achieves outstanding technique effect.Enable inventor pleasantly surprised
It is that, when inventor utilizes the method in the patent, it is logical to carry out the exhaust gas generated in the preprocessing process using jerusalem artichoke core as raw material
When entering the waste water containing methylene blue, it is found that fast degradation occurs for methylene blue in waste.
Further, inventor is tested the palliating degradation degree of methylene blue, finds the removal efficiency of methylene blue
Unexpectedly reached 100%.That is, the present invention is better than existing general solid base and liquid for the removal effect of methylene blue
Sill.Those skilled in the art open a kind of processing mode of novel methylene blue in waste it is found that the present invention is undoubtedly.
Although being obviously improved sugared conversion ratio in 103555774 B of CN, important tribute is made that for bio-ethanol industry
It offers.However, the technology in practical application, inevitably generate some exhaust gas, causes pollution to a certain extent.Therefore,
Meaning of the present invention also resides in, and solves the problems, such as the recycling of the exhaust gas in 103555774 B of CN.
Currently, the present inventor still tests to gas componant therein, and probe into pollutant therein
Cutting mechanisms, while also carrying out corresponding scale application improvement.
The w/v of the jerusalem artichoke core and methylene blue waste liquid is 1:0.5~2.Unless otherwise instructed, in the present invention
Signified w/v is g/mL or kg/L.
As a preferred solution of the present invention, the w/v of the jerusalem artichoke core and methylene blue waste liquid is 8:7.5
As a preferred solution of the present invention, the mass fraction of concentrated phosphoric acid is 65.0%, the mass fraction of hydrogen peroxide
It is 7.0%.
As the preferred embodiment of the present invention, when carrying out the degradation reaction, reaction temperature is 50~80 DEG C.
As a preferred solution of the present invention, when carrying out the degradation reaction, reaction temperature is 50 DEG C.Because at 50 DEG C
Under, the removal rate of pollutant is very outstanding, for the angle for saving reaction cost, carries out pollutant at such a temperature
Removal processing is both economical.
The degradation reaction is progress synchronous with the pretreatment, and it is described close to pre-process being passed through for generated exhaust gas synchronization
It closes and carries out degradation reaction in container, that is to say, that pretreatment time is the degradation reaction time.
In general, when carrying out the pretreatment of jerusalem artichoke core, the time of the pretreatment reaction is 1~5h.
As a preferred solution of the present invention, when carrying out the pretreatment of jerusalem artichoke core, the time of the pretreatment reaction is 4h.
Beneficial effects of the present invention:
The present invention has outstanding removal effect for common methylene blue, avoids existing solid base and liquid-based processing skill
Art needs the drawbacks of carrying out special modification to raw material, truly realize " with it is useless directly control it is useless " technical purpose,
Realize the combination of bio-ethanol preparation and two industries of wastewater treatment.
Specific implementation mode
The present invention is specifically described below by embodiment, it is necessary to which indicated herein is that following embodiment is only used
It is further detailed in the present invention, should not be understood as limiting the scope of the invention, which is skilled in technique
Personnel still fall within protection scope of the present invention according to some nonessential modifications and adaptations that foregoing invention content is made.
Embodiment 1
Jerusalem artichoke core be crushed into 40 mesh sieve, obtain jerusalem artichoke core powder;8g jerusalem artichoke core powder is put into reaction kettle, by solid-to-liquid ratio
It is 1:10 ratio, phosphoric acid and hydrogen peroxide solution 80g are added into reaction kettle, and the mass fraction of wherein concentrated phosphoric acid is
65.0%, the mass fraction of hydrogen peroxide is 7.0%, and pretreated temperature is 50 DEG C, pretreatment time 4h;Collect pretreatment
When the gas that generates;And gained gas is passed through equipped with the closed container in 7.5ml methylene blues waste liquid (100ppm) by synchronization
In (50ml specifications), degradation reaction is carried out in 50 DEG C.
Changed based on front and back reaction density, the removal rate of methylene blue is measured, and obtained removal rate is 100%.
Embodiment 2
The mass fraction for adjusting concentrated phosphoric acid is 70.0%, and the mass fraction of hydrogen peroxide is 5.0%, remaining keeps and implements
Example 1 is consistent.99% or more is still reached to the removal rate of methylene blue.
Embodiment 3
The weight for adjusting jerusalem artichoke core powder is 10g, and the volume of methylene blue waste liquid is 5ml, remaining keeps and embodiment 1 one
It causes.99% or more is still reached to the removal rate of methylene blue.
Embodiment 4
The weight for adjusting jerusalem artichoke core powder is 4g, and the volume of methylene blue waste liquid is 8ml, remaining keeps and embodiment 1 one
It causes.99% or more is still reached to the removal rate of methylene blue.
Claims (10)
1. the method for pre-processing produced exhaust-gas efficient removal methylene blue using jerusalem artichoke core, which is characterized in that the method includes
Following steps:
It collects jerusalem artichoke core and pre-processes produced exhaust gas, be passed through equipped in the closed container in methylene blue waste liquid, in 30~80 DEG C
Carry out degradation reaction;
The pretreated method of jerusalem artichoke core is:
Jerusalem artichoke core is put into reaction kettle, concentrated phosphoric acid-hydrogen peroxide mix reagent is added and carries out pretreatment reaction, wherein dense phosphorus
The mass fraction of acid is 60.0~70.0%, and the mass fraction of hydrogen peroxide is 5.0~8.0%.
2. according to the method described in claim 1, it is characterized in that, the w/v of the jerusalem artichoke core and methylene blue waste liquid
It is 1:0.5~2.
3. according to the method described in claim 2, it is characterized in that, the w/v of the jerusalem artichoke core and methylene blue waste liquid
It is 8:7.5.
4. according to the method described in claim 1, it is characterized in that, the mass fraction of concentrated phosphoric acid be 65.0%, hydrogen peroxide
Mass fraction is 7.0%.
5. according to the method described in claim 1, it is characterized in that, when carrying out the degradation reaction, reaction temperature is 50~80
℃。
6. according to the method described in claim 5, it is characterized in that, when carrying out the degradation reaction, reaction temperature is 50 DEG C.
7. according to claim 1~6 any one of them method, which is characterized in that the degradation reaction is and the pretreatment
It is synchronous to carry out, it pre-processes generated being passed through in the closed container for exhaust gas synchronization and carries out degradation reaction.
8. according to the method described in claim 1, it is characterized in that, carry out jerusalem artichoke core pretreatment when, the pretreatment reaction
Time is 1~5h.
9. according to the method described in claim 8, it is characterized in that, carry out jerusalem artichoke core pretreatment when, the pretreatment reaction
Time is 4h.
10. according to the method described in claim 1, it is characterized in that, the concentration of the water pollutant is at least 100ppm.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201810096865.0A CN108298661B (en) | 2018-01-31 | 2018-01-31 | Method for efficiently removing methylene blue by utilizing waste gas generated by jerusalem artichoke core pretreatment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201810096865.0A CN108298661B (en) | 2018-01-31 | 2018-01-31 | Method for efficiently removing methylene blue by utilizing waste gas generated by jerusalem artichoke core pretreatment |
Publications (2)
Publication Number | Publication Date |
---|---|
CN108298661A true CN108298661A (en) | 2018-07-20 |
CN108298661B CN108298661B (en) | 2020-05-26 |
Family
ID=62850810
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201810096865.0A Active CN108298661B (en) | 2018-01-31 | 2018-01-31 | Method for efficiently removing methylene blue by utilizing waste gas generated by jerusalem artichoke core pretreatment |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN108298661B (en) |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103508545A (en) * | 2013-09-10 | 2014-01-15 | 辽宁师范大学 | Method for degrading methylene blue with hydrogen peroxide under catalysis of graphene/MnO2 nano-composite |
CN104276650A (en) * | 2014-10-30 | 2015-01-14 | 黄俊潮 | Method for degrading methylene blue |
CN104923161A (en) * | 2015-07-09 | 2015-09-23 | 山东大学 | Preparation method of magnetic graphene oxide and application thereof |
CN107335402A (en) * | 2016-11-21 | 2017-11-10 | 德宏师范高等专科学校 | A kind of method of effectively absorption methylene blue in waste |
-
2018
- 2018-01-31 CN CN201810096865.0A patent/CN108298661B/en active Active
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103508545A (en) * | 2013-09-10 | 2014-01-15 | 辽宁师范大学 | Method for degrading methylene blue with hydrogen peroxide under catalysis of graphene/MnO2 nano-composite |
CN104276650A (en) * | 2014-10-30 | 2015-01-14 | 黄俊潮 | Method for degrading methylene blue |
CN104923161A (en) * | 2015-07-09 | 2015-09-23 | 山东大学 | Preparation method of magnetic graphene oxide and application thereof |
CN107335402A (en) * | 2016-11-21 | 2017-11-10 | 德宏师范高等专科学校 | A kind of method of effectively absorption methylene blue in waste |
Non-Patent Citations (1)
Title |
---|
郭兴杰: "《分析化学》", 31 August 2015 * |
Also Published As
Publication number | Publication date |
---|---|
CN108298661B (en) | 2020-05-26 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN105855275B (en) | A kind of processing method of sludge and kitchen garbage | |
CN107971324B (en) | Method and device for reducing and recycling kitchen waste anaerobic fermentation biogas residues | |
CN106430887B (en) | A kind of method of high solid content anaerobic sludge digestion methane phase | |
CN105349581A (en) | Full recycling method for producing methane and biogas residue activated carbon by utilizing medicine herb residue | |
CN107096500A (en) | A kind of utilization Chinese medicine slag prepares the method for magnetic bio charcoal, magnetic bio charcoal and application | |
CN111547903A (en) | Biochar-based micro-electrolysis filler and application thereof in chemical wastewater treatment | |
CN110157747A (en) | A kind of method of kitchen garbage processing and resource utilization | |
CN110451743A (en) | A kind of municipal wastewater plant excess sludge method of resource | |
CN107188293A (en) | Method for degrading organic pollutants by using manganese-zinc ferrite activated persulfate prepared from waste batteries | |
CN207375999U (en) | A kind of organic refuse treatment appts for coupling hydrothermal carbonization and biochemical reaction principle | |
CN107364942A (en) | It can be applied to hydro-thermal carbon composite, its preparation method and its application of class Fenton's reaction | |
CN106732332B (en) | A method of by coal ash for manufacturing for titanium doped mesopore silicon dioxide nano material | |
CN107354181A (en) | A kind of method for regulating and controlling debirs cooperative fermentation L lactic acid using cathodic reduction | |
CN102516322B (en) | Method for preparing levoglucosenone with magnetic solid phosphoric acid catalyst | |
CN108298661A (en) | The method that produced exhaust-gas efficient removes methylene blue is pre-processed using jerusalem artichoke core | |
CN106040241A (en) | Method for preparing heterogeneous Fenton catalyst from waste biogas residues and application | |
CN108408865A (en) | The method for removing methylene blue using the produced exhaust-gas efficient of stalk pretreatment | |
CN108383174A (en) | The method that produced exhaust-gas efficient removes paranitroanilinum is pre-processed using birch | |
CN108084098B (en) | A kind of circulation utilization method of nigrosine iron cement | |
CN108298663A (en) | The method that produced exhaust-gas efficient removes methylene blue is pre-processed using maize straw | |
CN108298662A (en) | The method that produced exhaust-gas efficient removes water pollutant is pre-processed using corncob | |
CN104843850A (en) | Method for treating industrial organic sewage | |
CN104651341A (en) | Method for performing bio-enzyme immobilization through rice bran | |
CN108178273A (en) | Utilize the method for Recalcitrant chemicals in bamboo scraps pretreatment exhaust gas removal water body | |
CN108341438A (en) | A kind of efficient method for removing Recalcitrant chemicals in water body |
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 | ||
GR01 | Patent grant | ||
GR01 | Patent grant |