CN109678221A - A kind of synergist and its preparation method and application for the sewage treatment of nonionic surfactant containing high concentration - Google Patents
A kind of synergist and its preparation method and application for the sewage treatment of nonionic surfactant containing high concentration Download PDFInfo
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- CN109678221A CN109678221A CN201811564297.9A CN201811564297A CN109678221A CN 109678221 A CN109678221 A CN 109678221A CN 201811564297 A CN201811564297 A CN 201811564297A CN 109678221 A CN109678221 A CN 109678221A
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- synergist
- nonionic surfactant
- high concentration
- sewage
- containing high
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- 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
- C02F1/285—Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
-
- 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
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
-
- 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
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/54—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
- C02F1/56—Macromolecular 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
- C02F2101/301—Detergents, surfactants
Abstract
The invention discloses a kind of synergist and its preparation method and application for the sewage treatment of nonionic surfactant containing high concentration.The synergist is prepared by the raw material of following weight percent: C1~C5Primary alkyl alcohol 1~10%, C1~C3Aldehyde material 1~30%, pH regulator 1~40%, amine polymer 1~20%, surplus is water.Synergist provided by the invention is high molecular polymer, it contains the anchoring groups such as a large amount of-OH ,-NH, COO-, the micelle that can be formed with nonionic surfactant in quick adsorption sewage, so as to simple, quick removal sewage middle and high concentration nonionic surfactant;Furthermore, after the synergist and PAC and PAM are used cooperatively, turbidity of sewage can be significantly reduced, 12NTU is reduced to by 1200NTU, water quality clear after processing, the synergist use process is simple, convenient, quick, and suitable for the processing of a large amount of high concentration nonionic surfactant sewage, application range is wide.
Description
Technical field
The present invention relates to technical field of sewage, living for non-ionic surface containing high concentration more particularly, to one kind
The synergist and its preparation method and application of property agent sewage treatment.
Background technique
Nonionic surfactant (NIS) has excellent blistering, wetting, emulsification and dispersion and unique potential resistance to electrolyte contamination
Performance, and it is widely used in the every field of national product life.With the development that it is applied, nonionic surfactant is useless
Water is also increasing year by year, and such waste water usually has the following characteristics that 1) Organic Pollutants in Wastewater is many kinds of, constituent is multiple
It is miscellaneous, concentration is high;2) Organic Pollutants in Wastewater is easy to combine other pollutants, generates New Complex type pollutant difficult to degrade;3)
Generally contain a large amount of emulsifier, detergent in waste water.Surfactant in waste water will cause water body blistering, generate toxicity,
Surfactant acts the reoxygenation rate and oxygenation degree steeped oneself-meeting and reduced in water in water, so that water quality is degenerated, influences aquatile
Existence, makes the self-purification of water be obstructed.Meanwhile surfactant can also emulsify other polluters in water body, increase polluter
Concentration, cause indirect pollution.In addition, a large amount of foam also will affect the settling property of sludge in waste water, to influence waste water
The treatment effeciency for the treatment of facility, thus it is very urgent to the improvement of nonionic surfactant waste water.
There is presently no the environmental quality standards of NIS and discharge standards, but consider its adverse effect to environment, exploitation
Effective processing technique is also very important out.Currently used processing method mainly includes foamet, absorption method, life
Object method, micro-electrolysis method, Fenton oxidation method or a variety of methods are used in combination.Such as patent CN201410524699.1 is provided
Method be that the pH value of sewage is first adjusted with sulfuric acid, add ferric sulfate catalyst, and carry out electrolysis processing, method not only mistake
Journey is complicated, cumbersome, can not handle a large amount of waste water, and strong acid is utilized, treated sewage also needs at additional deacidification
Reason could discharge, cost of sewage disposal height etc..
Not only process is complicated for the processing technique of currently used sewage middle and high concentration nonionic surfactant, is not suitable for
The processing of large amount of sewage;And processing cost is high, and the water body for being largely unsatisfactory for discharge standard is caused to enter the Nature, pollutes ring
Border.Therefore, it is necessary to provide, one kind is low in cost, and use process is simple, convenient, and is suitable for a large amount of high concentration non-ionic surfaces
The product of activating agent sewage treatment.
Summary of the invention
The purpose of the present invention is to provide a kind of synergist for the sewage treatment of nonionic surfactant containing high concentration.
The micelle that synergist of the present invention can be formed with nonionic surfactant in quick adsorption sewage, to reach quick, simple
The nonionic surfactant of single removal sewage middle and high concentration, can significantly reduce the turbidity of sewage, treated clarifying contaminated liquids
Transparent, the impurity in sewage substantially reduces, and alleviates the pressure of sewage subsequent purification processing;The application of synergist of the present invention
Pollution and destruction of the nonionic surfactant direct emission for environment in sewage can be reduced, the protection of environment is conducive to.
Another object of the present invention is to provide the increasings for the sewage treatment of nonionic surfactant containing high concentration
Imitate the preparation method of agent.
A further object of the present invention is to provide the increasings for the sewage treatment of nonionic surfactant containing high concentration
Imitate the application of agent.
Above-mentioned purpose of the invention is achieved by following scheme:
A kind of synergist for the sewage treatment of nonionic surfactant containing high concentration, the synergist is by following weight percent
The raw material of ratio is prepared: C1~C5Primary alkyl alcohol 1~10%, C1~C3Aldehyde material 1~30%, pH regulator 1~40%,
Amine polymer 1~20%, surplus are water.
Synergist provided by the invention is high molecular polymer, and the high molecular polymer is existed by the raw material of aforementioned proportion
Polycondensation reaction occurs under specified conditions and is prepared, the high molecular polymer contains the anchoring base such as a large amount of-OH ,-NH, COO-
Group, the micelle that can be formed with nonionic surfactant in quick adsorption sewage, so as in simple, quick removal sewage
High concentration nonionic surfactant, and the high molecular polymer is suitable for a large amount of high concentration nonionic surfactant sewage
Processing, application range is wide.
Preferably, the synergist is prepared by the raw material of following weight percent: C1~C5Primary alkyl alcohol 1~3%,
C1~C3Aldehyde material 5~10%, pH regulator 3~8%, amine polymer 5~15%, surplus is water.
Preferably, the C1~C5Primary alkyl alcohol be selected from isopropanol, n-butanol, methanol, ethyl alcohol, glycerine, ethylene glycol or
One or both of butanediol;The C1~C3Aldehyde material be selected from formaldehyde, benzaldehyde, glyoxal or 3- aminobenzaldehyde
One of polymer is a variety of;The pH regulator is selected from formic acid, acetic acid, hydrochloric acid, sulfuric acid, ethanedioic acid, nitrilotriacetic acid or ammonia
One of base sulfonic acid is a variety of;The amine polymer is selected from ethylenediamine, dicyandiamide, melamine, urea or six methines
One or both of tetramine.
The present invention also protects the system of the synergist for the sewage treatment of nonionic surfactant containing high concentration simultaneously
After mixing the raw material in proportion, under the conditions of 60~80 DEG C polycondensation reaction occurs for Preparation Method, and target production can be prepared
Object.
Preferably, the time of the polycondensation reaction is 1~3h.
The preparation process of the synergist is simple, low for equipment and condition requirement, is convenient for large-scale production, is conducive to
It is promoted and applied.
The application of the synergist for the sewage treatment of nonionic surfactant containing high concentration is also in guarantor of the invention
It protects in range.
Preferably, the synergist for the sewage treatment of nonionic surfactant containing high concentration is for removing in sewage
Nonionic surfactant.
Preferably, the synergist is used cooperatively with PAC and PAM.
Preferably, PAC is first added into sewage to be uniformly mixed, the synergist is then added and is uniformly mixed, and adjust mixed
Liquid pH value is closed to 7~8, PAM is finally added and is uniformly mixed, generate cotton-shaped alum slag, filtering.
After synergist of the present invention and PAC and PAM are used cooperatively, it can significantly lower the turbidity of sewage, water after processing
Matter clear, the impurity in sewage substantially reduce, alleviate the pressure of sewage subsequent purification processing, and the synergist makes
It is simple, convenient with process, it works quick.
Compared with prior art, the invention has the following advantages:
Synergist provided by the invention is high molecular polymer, contains the anchoring groups such as a large amount of-OH ,-NH- ,-COO-, can be with
The micelle that nonionic surfactant is formed in quick adsorption sewage, so as to simple, quick removal sewage middle and high concentration
Nonionic surfactant;In addition, can make after the synergist and PAC and PAM are used cooperatively containing high concentration nonionic table
The turbidity of sewage of face activating agent significantly reduces, and is reduced to 12NTU by 1200NTU, water quality is as clear as crystal after processing, alleviates sewage
The pressure of subsequent purification processing;The application of synergist of the present invention can reduce nonionic surfactant direct emission in sewage
Pollution and destruction for environment, are conducive to the protection of environment.
In addition, the use process of the synergist is simple, convenient, works quickly, be suitable for a large amount of high concentration nonionic tables
The processing of face activating agent sewage, application range are wide.
Detailed description of the invention
Fig. 1 is raw sewerage and through PAC+PAM treated comparison diagram, and wherein left figure is untreated dirt
Water sample, right figure are through PAC+PAM treated sewage sample.
Fig. 2 is raw sewerage and through treated the comparison diagram of experimental group 1, and wherein left figure is untreated dirt
Water sample, right figure are through treated the sewage sample of experimental group 1.
Fig. 3 is raw sewerage, after PAC+PAM is handled, control group 1 and experimental group 1 treated comparison diagram.
Fig. 4 is through treated the effect picture of control group 5.
Fig. 5 is the comparison diagram after raw sewerage and experimental group 1 treated sewage water filtration, and wherein left figure is not locate
Effect after the sewage sample filtering of reason, right figure are filtered effect after experimental group 1 is handled.
Specific embodiment
The present invention is made combined with specific embodiments below and further being elaborated, the embodiment is served only for explaining this
Invention, is not intended to limit the scope of the present invention.Test method as used in the following examples is normal unless otherwise specified
Rule method;Used material, reagent etc., unless otherwise specified, for the reagent and material commercially obtained.
Embodiment 1
A kind of synergist for the sewage treatment of nonionic surfactant containing high concentration, is prepared by following raw material and process
It arrives:
(1) weigh raw material according to mass percent: melamine 12%, formaldehyde 10%, ethylene glycol 5%, formic acid 15%, surplus are
Water;
(2) 70 DEG C are heated water to, remaining whole raw material mixing, stirring then will be entered, polycondensation reaction 2h occurs for heat preservation
Obtain the synergist.
Embodiment 2
A kind of synergist for the sewage treatment of nonionic surfactant containing high concentration, preparation process with embodiment 1, difference
Be in the raw material for using following mass percent: melamine 6%, formaldehyde 8%, glycerine 2%, hydrochloric acid 5%, surplus is water;Instead
Answering temperature is 60 DEG C, reaction time 1.5h.
Embodiment 3
A kind of synergist for the sewage treatment of nonionic surfactant containing high concentration, preparation process with embodiment 1, difference
It is in the raw material using following mass percent: hexamethylenetetramine 8%, glyoxal 15%, methanol 2%, sulfamic acid 10%, remaining
Amount is water;Reaction temperature is 60 DEG C, reaction time 3h.
Embodiment 4
A kind of synergist for the sewage treatment of nonionic surfactant containing high concentration, preparation process with embodiment 1, difference
It is in the raw material using following mass percent: urea 10%, 3- aminobenzoic aldehyde polymer 8%, glycerine 1%, nitrilotriacetic acid
15%, surplus is water;Reaction temperature is 80 DEG C, reaction time 1.5h.
Embodiment 5
A kind of synergist for the sewage treatment of nonionic surfactant containing high concentration, preparation process with embodiment 1, difference
It is in the raw material using following mass percent: melamine 10%, 3- aminobenzoic aldehyde polymer 8%, glycerine 1%, hydrochloric acid
15%, surplus is water;Reaction temperature is 70 DEG C, reaction time 1.5h.
Embodiment 6
A kind of synergist for the sewage treatment of nonionic surfactant containing high concentration, preparation process with embodiment 1, difference
Be in the raw material for using following mass percent: melamine 12%, glyoxal 8%, glycerine 1%, hydrochloric acid 15%, surplus for
Water;Reaction temperature is 70 DEG C, reaction time 1.5h.
Comparative example 1
A kind of synergist for the sewage treatment of nonionic surfactant containing high concentration, preparation process with embodiment 1, difference
Be in the raw material for using following mass percent: melamine 30%, formaldehyde 8%, glycerine 2%, hydrochloric acid 5%, surplus is water;Instead
Answer temperature 60 C, reaction time 3h.
Since content of melamine is excessively high, product directly solidifies, and can not prepare target product.
Comparative example 2
A kind of synergist of the sewage treatment for the nonionic surfactant containing high concentration, using reactant and corrresponding quality point
It counts with embodiment 1, the difference is that, 50 DEG C are heated water to, after all reactants are added, keeps the temperature 2h.
Since temperature is too low, lead to not react, target product can not be prepared.
Comparative example 3
A kind of synergist of the sewage treatment for the nonionic surfactant containing high concentration, preparation process are different with embodiment 1
Place is to use the raw material of following mass percent: melamine 6%, formaldehyde 8%, hydrochloric acid 5%, surplus is water;Reaction temperature 60
DEG C, reaction time 3h.
Efficacy test
The synergist prepared using embodiment 2,3,4 and comparative example 3 as test object, test its remove sewage middle and high concentration it is non-from
The effect of sub- surfactant.
Test method are as follows: using the cleaning liquid of certain stainless steel cleaning factory, it is known that in the sample containing it is a large amount of it is non-from
Sub- surfactant causes the electrostatic neutralization of PAC that can not play effect since nonionic surfactant micelle is not charged
Fruit can not make haze reduction.So in this experiment, using turbidity variation as the mark of the removal effect of nonionic surfactant
Will.Turbidity is tested using UV-visible spectrophotometry.
Experimental group 1: the synergist prepared using embodiment 2, PAC+ synergist+PAM processing.
Experimental group 2: synergist prepared with embodiment 3, PAC+ synergist+PAM processing are adopted.
Experimental group 3: the synergist prepared using embodiment 4, PAC+ synergist+PAM processing.
Control group 1: the synergist prepared using embodiment 2 is only added synergist and is handled.
Control group 2: adopting synergist prepared with embodiment 3, only adds synergist and is handled.
Control group 3: the synergist prepared using embodiment 4 is only added synergist and is handled.
Control group 4:PAC+PAM processing.
Control group 5: the synergist prepared using comparative example 3, PAC+ synergist+PAM processing.
Shown in test result is as follows table 1 and Fig. 1~5.Wherein Fig. 1 is the effect that synergist processing is not used, wherein left figure
For untreated sewage sample, right figure is treated the effect of control group 4;Fig. 2 is the effect handled using synergist, wherein left
Figure is untreated sewage sample, and right figure is treated the effect of experimental group 1, it can be seen that after processing, it is non-in sewage
Ionic surface active agent is condensed into cotton-shaped alum slag, and directly filtering can remove cotton-shaped alum slag, and filtered sewage is as clear as crystal;Figure
The synergy for being followed successively by untreated sewage sample in 3 from left to right, being prepared through PAC+PAM processing (i.e. control group 4), embodiment 2
Agent handles the result of the synergist+PAC+PAM processing (i.e. experimental group 1) of (i.e. control group 1) and the preparation of embodiment 2 (due to experiment
The effect of group 1,2 and 3 is suitable, therefore only provides the treatment effect figure of experimental group 1), as can be known from Fig. 3, only with the present invention
When the synergist or PAC+PAM of preparation, the nonionic surfactant in sewage can not be precipitated;And work as increasing of the present invention
When effect agent and PAC, PAM are used cooperatively, it can be very good the nonionic surfactant in precipitating sewage, reduce the turbid of sewage
Degree.Fig. 4 is treated the effect of control group 5, it can be seen that the synergist prepared through reference examples 3 is used cooperatively with PAC, PAM
When, a part of nonionic surfactant can be precipitated, but ineffective, its turbidity of treated sewage is still very high, with
Only with PAC+PAM, treated that effect is suitable in control group 4.Fig. 5 is raw sewerage and treated through experimental group 1
Comparison diagram after sewage water filtration, wherein left figure is the effect picture of raw sewerage filtering, and right figure is after the processing of experimental group 1
Sewage water filtration effect picture, from the comparison of two width figures it is found that filtering out cotton-shaped alum slag through treated the sewage of experimental group 1,
Sewage is as clear as crystal, and nonionic surfactant therein almost removes.
The sewage to be measured of table 1 before treatment after turbidity comparing result
It is found that only high concentration ought be contained with PAC+PAM processing with synergist prepared by the present invention or only from table 1 and Fig. 1~3
When the sewage of nonionic surfactant, the nonionic surfactant in sewage, after processing, sewage can not be removed well
Turbidity there is no too big variation, it is dirty after processing and when synergist and PAC, PAM prepared by embodiment 1 to 3 is used cooperatively
The turbidity conspicuousness of water reduces, and turbidity is only 1/10th or so before handling, and treated, and sewage is as clear as crystal, table
When bright synergist of the present invention and PAC, PAM are used cooperatively, the nonionic surfactant in sewage, effect can be effectively removed
Significantly, can extensive mass processing nonionic surfactant containing high concentration sewage, it is living to reduce non-ionic surface in sewage
Property agent discharge amount, reduce pollution and destruction of the nonionic surfactant to environment, be conducive to the protection of environment.
After from the comparison of experimental group 1~3 and control group 4, control group 5 it is found that control group 4 and control group 5 handle, sewage
Turbidity is suitable, shows the synergist not prepared according to the method for the invention, when being used cooperatively with PAC, PAM, does not show
Synergistic effect is not suitable for the purified treatment of the nonionic surfactant containing high concentration in sewage.
Finally, it should be noted that the above embodiments are merely illustrative of the technical solutions of the present invention rather than protects to the present invention
The limitation of shield range can also be made on the basis of above description and thinking for those of ordinary skill in the art
Other various forms of variations or variation, there is no necessity and possibility to exhaust all the enbodiments.It is all of the invention
Made any modifications, equivalent replacements, and improvements etc., should be included in the protection of the claims in the present invention within spirit and principle
Within the scope of.
Claims (8)
1. a kind of synergist for the sewage treatment of nonionic surfactant containing high concentration, which is characterized in that the synergist
It is prepared by the raw material of following weight percent: C1~C5Primary alkyl alcohol 1~10%, C1~C3Aldehyde material 1~30%,
PH regulator 1~40%, amine polymer 1~20%, surplus are water.
2. being used for the synergist of the sewage treatment of nonionic surfactant containing high concentration according to claim 1, feature exists
In the synergist is prepared by the raw material of following weight percent: C1~C5Primary alkyl alcohol 1~3%, C1~C3Aldehydes
Substance 5~10%, pH regulator 3~8%, amine polymer 5~15%, surplus are water.
3. the synergist according to claim 1 or claim 2 for the sewage treatment of nonionic surfactant containing high concentration, feature
It is, the C1~C5Primary alkyl alcohol in isopropanol, n-butanol, methanol, ethyl alcohol, glycerine, ethylene glycol or butanediol
It is one or two kinds of;The C1~C3Aldehyde material in formaldehyde, benzaldehyde, glyoxal or 3- aminobenzoic aldehyde polymer
It is one or more;The pH regulator is in formic acid, acetic acid, hydrochloric acid, sulfuric acid, ethanedioic acid, nitrilotriacetic acid or sulfamic acid
It is one or more;The amine polymer in ethylenediamine, dicyandiamide, melamine, urea or hexamethylenetetramine one
Kind or two kinds.
4. the preparation method of the synergist as claimed in claim 1 or 2 for the sewage treatment of nonionic surfactant containing high concentration,
It is characterized in that, polycondensation reaction occurs under the conditions of 60~80 DEG C, mesh can be prepared after the raw material is mixed in proportion
Mark product.
5. the preparation side for the synergist of the sewage treatment of nonionic surfactant containing high concentration according to claim 4
Method, which is characterized in that the time of the polycondensation reaction is 1~3h.
6. the application of the synergist as claimed in claim 1 or 2 for the sewage treatment of nonionic surfactant containing high concentration, special
Sign is, for removing the nonionic surfactant in sewage.
7. the application for the synergist of the sewage treatment of nonionic surfactant containing high concentration according to claim 6,
It is characterized in that, the synergist is used cooperatively with PAC and PAM.
8. the application for the synergist of the sewage treatment of nonionic surfactant containing high concentration according to claim 7,
It is characterized in that, PAC is first added into sewage and is uniformly mixed, it is equal that any synergist mixing of Claims 1 to 4 is then added
It is even, and mixed liquor pH value is adjusted to 7~8, it finally adds PAM and is uniformly mixed, generate cotton-shaped alum slag, filtering.
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Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH06262184A (en) * | 1993-03-12 | 1994-09-20 | Kanebo Nsc Ltd | Waste water disposal |
JP2008161769A (en) * | 2006-12-27 | 2008-07-17 | Hakuto Co Ltd | Method for treating waste water |
CN107879531A (en) * | 2017-11-21 | 2018-04-06 | 四川理工学院 | The recovery process of surfactant in waste water |
CN107902828A (en) * | 2017-11-21 | 2018-04-13 | 四川理工学院 | The recovery method of Coal Gas Washing Cycling Water nonionic surfactant |
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2018
- 2018-12-20 CN CN201811564297.9A patent/CN109678221B/en active Active
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH06262184A (en) * | 1993-03-12 | 1994-09-20 | Kanebo Nsc Ltd | Waste water disposal |
JP2008161769A (en) * | 2006-12-27 | 2008-07-17 | Hakuto Co Ltd | Method for treating waste water |
CN107879531A (en) * | 2017-11-21 | 2018-04-06 | 四川理工学院 | The recovery process of surfactant in waste water |
CN107902828A (en) * | 2017-11-21 | 2018-04-13 | 四川理工学院 | The recovery method of Coal Gas Washing Cycling Water nonionic surfactant |
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