CN106277237B - A kind of method of heterotroph in control loop cooling water - Google Patents
A kind of method of heterotroph in control loop cooling water Download PDFInfo
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- CN106277237B CN106277237B CN201510350245.1A CN201510350245A CN106277237B CN 106277237 B CN106277237 B CN 106277237B CN 201510350245 A CN201510350245 A CN 201510350245A CN 106277237 B CN106277237 B CN 106277237B
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Abstract
The present invention relates to a kind of methods of heterotroph in control loop cooling water, comprising: (1) chlorine system fungicide and a effective amount of chlorine residue stabilizer is continuously added into recirculated cooling water, the chlorine residue stabilizer is the amine and/or hydramine that boiling point is greater than 100 DEG C；(2) when the heterotrophism bacterial content in recirculated cooling water is greater than Con trolling index value, quaternary ammonium salt non-oxidative antimicrobial is added to impact type.It, can heterotroph effectively in control loop cooling water using method of the invention.
Description
Technical field
The present invention relates to a kind of methods of heterotroph in control loop cooling water.
Background technique
Recirculating cooling water system is a special water body environment, temperature (generally 25 DEG C~40 DEG C) and pH value (one
As be 6.5~9.0), sufficient dissolved oxygen and illumination, and bring enriches minerals and organic matter due to concentration, is a variety of
Microorganism provides suitable growth conditions, for example bacterium (such as der Pilz produces slime bacteria, pityrosporion ovale, acid-producing bacteria), fungi are (such as
Saccharomycete, mould), algae (such as diatom, green alga) and protozoan (such as amoeba, infusorian) can be in circulating cooling water system
It is bred in system.
The mass propagation of microorganism can seriously affect the normal operation of recirculating cooling water system, main harm show with
Lower three aspects.
One, biological clay is generated
Microorganism is during own growth is bred, to a large amount of stickum of cell exocrine, these stickums
Biological clay can be collectively formed in conjunction with particulate matter, ion and the grains of sand etc. in water.And biological clay will lead to: (1) reducing cold
The heat exchange efficiency of exchange device；(2) aggravate the corrosion of cold exchange device；(3) block pipeline, increase resistance of water conveyance, reduce efficiency；(4)
Increase water supply production cost.
Two, itself caused corrosion of microorganism
Microorganism can generate various types of acid in metabolic processes, and if sulfur bacteria generates sulfuric acid, nitrifier is generated
Nitrous acid and nitric acid, sulfate reducing bacteria generate H2S, there are also other bacteriums can generate acetic acid, lactic acid, oxalic acid, citric acid and Portugal
The organic acids such as grape acid, these acids can all make water quality composition change and cause metal erosion；The growth of iron bacteria, solvable
Property Fe2+It is oxidized to Fe (OH)3, corrode iron.Therefore microbial growth can inherently promote the generation of corrosion.
Three, decomposition of the microorganism to water treatment agent
Corrosion inhibiter and antisludging agent are largely organic matter, typically contain carbon, nitrogen and phosphorus element, can be as microorganism new old generation
The growth of carbon source, nitrogen source and the phosphorus source thanked, microorganism can consume these corrosion inhibiter and antisludging agent, lead to the reduction of its drug effect.
In order to guarantee that industrial circulating cooling water system safely, effectively is run, it is necessary to the microorganism in recirculated cooling water
Strict control is carried out, adding fungicide is most effective, most common control method.Fungicide type, the property (pH value of cooling water
And the chemical substance contained), add the factors such as concentration, dosing method and can all influence bactericidal effect；In addition, certain fungicide may be used also
It can bring and other aspect problems such as decompose corrosion inhibiting and descaling agent, make turbidity of circulating water increase；Therefore cold to recycling in selection fungicide
But when the microorganism in water is controlled, need to comprehensively consider various factors.
Fungicide can be divided into oxidizing bactericide and non oxidizing bactericide.Chlorine system fungicide is (secondary by generating in water
Chlorate anions is sterilized) be a kind of low cost, broad spectrum activity Strong oxdiative fungicide, make in industrial Open recirling cooling water system
With most generally.Quaternary ammonium salt non oxidizing bactericide has itself unique advantage in terms of sterilization, but in large dosage in use, can lead
Circulation turbidity is caused to dramatically increase, it is necessary to which large excretion and large complement are replaced, by the haze reduction of recirculated water to normal value.
When with microorganism in fungicide control loop cooling water, generally various sterilization agent can be selected to be used cooperatively, one
Kind dosing method is thrown by the way of continuous or impact type using a kind of inexpensive, broad spectrum activity fungicide as sterilization host agent
Add；Using other fungicide as sterilization adjuvant, when microorganism cannot be effectively controlled, using the side of impact type, large dosage
Formula adds (dosage is generally 100mg/L~150mg/L).
Fungicide in recirculating cooling water system, other than due to normal consumption caused by sterilizing, there is also other aspects
Caused non-normal consumption needs constantly to add medicament on the one hand in order to compensate for reagent consumption；On the other hand in order to reduce medicine
Agent cost there is a need the non-normal consumption for controlling medicament.CN1535250A discloses a kind of micro- for controlling in aqueous solution
The growth of biology or the method for killing microorganism, this method are referred to halogen stabilizer, such as uride, urea, sulfonamide, sulfonyl
Amine, pyrroles, indoles, imidazoline, melamine, amino-acid ester, pyrimidine, phosphamide, thiazole, pyrrolidones, sulfamic acid, ammonia,
Ammonium bromide etc. is improved the photodissociation and oxidation stability of fungicide by using these halogen stabilizers, however is being applied to open
When open cycle cooling water system, these halogen stabilizers are simultaneously not always effective, additionally, there may be " halogen source and ammonium salt or
The halogen stabilizers such as urea and sulfamic acid or sulfamate react to each other and lose " the problem of.This method, which is mentioned that, " to be used
Quaternary ammonium biocide or the amine of biocidal are come the effect of increasing biocidal system ".The mechanism and quaternary ammonium salt of organic amine biocidal
Seemingly, based on the purpose of biocidal, the amine of biocidal is usually the fatty amine for having Long carbon chain, such as containing more than 12 carbon long
Chain, the primary amine for being insoluble in water.
In some cases, such as when recirculated water contains NH4 +When, nitrococcus is easily bred, and it is out of control to often result in microorganism at this time
(basicity and pH value sharply decline) is dramatically increased with Circulating Water Corrosion.At this point, general add the frequency using increase fungicide
With dosage or increase the measure replaced to water body of blowdown and cope with, these measures in addition to causing with water cost and/or
Outside reagent cost (fungicide and/or corrosion inhibiting and descaling agent) increases, nitrococcus breeding still can not be effectively controlled sometimes (as used chlorine
It is fungicide, even if increasing added amount of chemical, it is also difficult to detect chlorine residue), and be also possible to bring otherwise problem (such as
Using quaternary ammonium salt non oxidizing bactericide, it will lead to circulation turbidity and dramatically increase).
Summary of the invention
For these problems of the existing technology, the present invention provides a kind of sides of chlorine residue in stable recirculated cooling water
A kind of method of microorganism in method, control loop cooling water, in a kind of control loop cooling water heterotroph method and a kind of control
The method of nitrococcus in recirculated cooling water processed.
Specifically, the present invention includes the following contents.
(1) method stablized the method for chlorine residue and control microorganism
1, in a kind of stable recirculated cooling water chlorine residue method, be included in recirculated cooling water addition chlorine system fungicide,
It is characterized in that, a effective amount of chlorine residue stabilizer is added into recirculated cooling water, and the chlorine residue stabilizer is that boiling point is greater than 100 DEG C
Amine and/or hydramine.
2, the method according to 1, which is characterized in that chlorine system fungicide and the chlorine residue stabilizer are in recirculated water cooling
But in water system to add position different and/or add time difference.
3, according to aforementioned any method, which is characterized in that chlorine system fungicide is added with the chlorine residue stabilizer
Mode is continuously to add.
4, according to aforementioned any method, which is characterized in that chlorine residue stabilizer is formed first with anti-incrustation corrosion inhibitor and is mixed
Then first mixture is continuously added in recirculated cooling water by object.
5, the method according to 4, which is characterized in that in first mixture, quality shared by chlorine residue stabilizer point
Number is 0.5%~10%, preferably 1%~8%, further preferred 2%~5%.
6, the method according to 4 or 5, which is characterized in that the dosage of first mixture makes its relative cycle water
Mass concentration 50mg/L~150mg/L, preferably 80mg/L~120mg/L.
7, according to aforementioned any method, which is characterized in that the chlorine residue stabilizer is selected from di-n-propylamine, amylamine, second two
Amine, 1,2- propane diamine, 1,3- propane diamine, 1,4- butanediamine, 1,5- pentanediamine, 1,6- hexamethylene diamine, diethylenetriamine, triethylene four
Amine, tetraethylenepentamine, pentaethylene hexamine, ethanol amine, diethanol amine, triethanolamine, N, N- dimethylethanolamine, N- methyl diethyl
One of hydramine, N- diethyl ethylene diamine, n-propanolamine, isopropanolamine, diisopropanolamine (DIPA) and triisopropanolamine or it is any
Combination.
8, according to aforementioned any method, which is characterized in that chlorine system fungicide is selected from liquid chlorine, sodium hypochlorite, secondary
Calcium chlorate, dichlord isocyanurice acid (one of Puritabs, sym-closene (strong chlorine oil) or its arbitrary combination.
9, according to aforementioned any method, which is characterized in that the dosage of chlorine system fungicide makes in recirculated cooling water
Chlorine residue mass concentration reaches 0.5mg/L~2mg/L, preferably 1mg/L~1.5mg/L.
10, according to aforementioned any method, which is characterized in that contain or not contain ammonia nitrogen in the recirculated cooling water.
11, in a kind of control loop cooling water microorganism method, including with the use of chlorine system fungicide and non-oxide kill
Microbial inoculum, which is characterized in that residual chlorine concentration is stablized using aforementioned any method.
12, the method according to 11, which is characterized in that the dosing method of the non-oxidative antimicrobial is impact type throwing
Add.
This method is especially suitable for Open recirling cooling water system.
(2) method of heterotroph is controlled
1, in a kind of control loop cooling water heterotroph method, comprising: (1) chlorine system is continuously added into recirculated cooling water
Fungicide and a effective amount of chlorine residue stabilizer, the chlorine residue stabilizer are the amine and/or hydramine that boiling point is greater than 100 DEG C；(2) when
When heterotrophism bacterial content in recirculated cooling water is greater than Con trolling index value, quaternary ammonium salt non-oxidative antimicrobial is added to impact type.
2, the method according to 1, which is characterized in that chlorine system fungicide and the chlorine residue stabilizer are in recirculated water cooling
But position difference is added in water system.
3, according to aforementioned any method, which is characterized in that chlorine residue stabilizer is formed first with anti-incrustation corrosion inhibitor and is mixed
Then first mixture is continuously added in recirculated cooling water by object.
4, the method according to 3, which is characterized in that in first mixture, quality shared by chlorine residue stabilizer point
Number is 0.5%~10%, preferably 1%~8%, further preferred 2%~5%.
5, the method according to 3 or 4, which is characterized in that the dosage of first mixture makes its relative cycle water
Mass concentration 50mg/L~150mg/L, preferably 80mg/L~120mg/L.
6, according to aforementioned any method, which is characterized in that the chlorine residue stabilizer is selected from di-n-propylamine, amylamine, second two
Amine, 1,2- propane diamine, 1,3- propane diamine, 1,4- butanediamine, 1,5- pentanediamine, 1,6- hexamethylene diamine, diethylenetriamine, triethylene four
Amine, tetraethylenepentamine, pentaethylene hexamine, ethanol amine, diethanol amine, triethanolamine, N, N- dimethylethanolamine, N- methyl diethyl
One of hydramine, N- diethyl ethylene diamine, n-propanolamine, isopropanolamine, diisopropanolamine (DIPA) and triisopropanolamine or it is any
Combination.
7, according to aforementioned any method, which is characterized in that chlorine system fungicide is selected from liquid chlorine, sodium hypochlorite, secondary
Calcium chlorate, dichlord isocyanurice acid (one of Puritabs, sym-closene (strong chlorine oil) or its arbitrary combination.
8, according to aforementioned any method, which is characterized in that the dosage of chlorine system fungicide makes in recirculated cooling water
Chlorine residue mass concentration reaches 0.5mg/L~2mg/L, preferably 1mg/L~1.5mg/L.
9, according to aforementioned any method, which is characterized in that contain or not contain ammonia nitrogen in the recirculated cooling water.
10, according to aforementioned any method, which is characterized in that the heterotrophism bacterial content in step (2), in recirculated cooling water
When between 10 times greater than Con trolling index value to Con trolling index value, quaternary ammonium salt non-oxidative antimicrobial, institute are added to impact type
Concentration 2mg/L~20mg/L that the dosage of quaternary ammonium salt non-oxidative antimicrobial makes it in recirculated cooling water is stated, preferably
5mg/L~15mg/L；After quaternary ammonium salt non oxidizing bactericide is added, recirculating cooling water system does not force blowdown progress water body to be set
It changes and continuous operation.
11, according to aforementioned any method, which is characterized in that the quaternary ammonium salt non oxidizing bactericide has following
Structure:
The wherein integer that n is 10~18, preferably 12 or 14；The integer that m is 8~12；X-Selected from Cl-Or Br-。
This method is especially suitable for Open recirling cooling water system.
(3) method of nitrococcus is controlled
1, in a kind of control loop cooling water nitrococcus method, comprising: (1) chlorine is continuously added into recirculated cooling water
It is fungicide and a effective amount of chlorine residue stabilizer, the chlorine residue stabilizer is the amine and/or hydramine that boiling point is greater than 100 DEG C；(2)
As the NO in recirculated cooling water2 -When content >=1mg/L, quaternary ammonium salt non-oxidative antimicrobial is added to impact type.
2, the method according to 1, which is characterized in that chlorine system fungicide and the chlorine residue stabilizer are in recirculated water cooling
But position difference is added in water system.
3, according to aforementioned any method, which is characterized in that chlorine residue stabilizer is formed first with anti-incrustation corrosion inhibitor and is mixed
Then first mixture is continuously added in recirculated cooling water by object.
4, the method according to 3, which is characterized in that in first mixture, quality shared by chlorine residue stabilizer point
Number is 0.5%~10%, preferably 1%~8%, further preferred 2%~5%.
5, the method according to 3 or 4, which is characterized in that the dosage of first mixture makes its relative cycle water
Mass concentration 50mg/L~150mg/L, preferably 80mg/L~120mg/L.
6, according to aforementioned any method, which is characterized in that the chlorine residue stabilizer is selected from di-n-propylamine, amylamine, second two
Amine, 1,2- propane diamine, 1,3- propane diamine, 1,4- butanediamine, 1,5- pentanediamine, 1,6- hexamethylene diamine, diethylenetriamine, triethylene four
Amine, tetraethylenepentamine, pentaethylene hexamine, ethanol amine, diethanol amine, triethanolamine, N, N- dimethylethanolamine, N- methyl diethyl
One of hydramine, N- diethyl ethylene diamine, n-propanolamine, isopropanolamine, diisopropanolamine (DIPA) and triisopropanolamine or it is any
Combination.
7, according to aforementioned any method, which is characterized in that chlorine system fungicide is selected from liquid chlorine, sodium hypochlorite, secondary
Calcium chlorate, dichlord isocyanurice acid (one of Puritabs, sym-closene (strong chlorine oil) or its arbitrary combination.
8, according to aforementioned any method, which is characterized in that the dosage of chlorine system fungicide makes in recirculated cooling water
Chlorine residue mass concentration reaches 0.5mg/L~2mg/L, preferably 1mg/L~1.5mg/L.
9, according to aforementioned any method, which is characterized in that contain or not contain ammonia nitrogen in the recirculated cooling water.
10, according to aforementioned any method, which is characterized in that in step (2), the NO in recirculated cooling water2 -Content is
When 1mg/L~3mg/L, quaternary ammonium salt non-oxidative antimicrobial, the throwing of the quaternary ammonium salt non-oxidative antimicrobial are added to impact type
Dosage makes its concentration 2mg/L~20mg/L in recirculated cooling water, preferably 5mg/L~15mg/L；It is non-that quaternary ammonium salt is added
After oxidizing bactericide, recirculating cooling water system does not force blowdown to carry out water substitution and continuous operation.
11, according to aforementioned any method, which is characterized in that the quaternary ammonium salt non oxidizing bactericide has following
Structure:
The wherein integer that n is 10~18, preferably 12 or 14；The integer that m is 8~12；X-Selected from Cl-Or Br-。
This method is especially suitable for Open recirling cooling water system.
Compared with prior art, the present invention has the following advantages that.
Although the photodissociation and oxidation stability of fungicide 1, have been improved using halogen stabilizer in the prior art,
When being applied to Open recirling cooling water system, there is also the fungicide non-normal consumptions of other forms, keep these halogens steady
Determine agent and not always effectively, for example when using ammonia as halogen stabilizer, chlorine residue can still result in fungicide by circulating water cooling tower stripping
Dosage increases；Chlorine residue stabilizer of the invention can effectively solve the technical problem.
2, the prior art adds corrosion inhibiting and descaling agent and chlorine system fungicide in the different location of recirculating cooling water system respectively, with
It avoids the medicament of high concentration from contacting with each other, leads to higher medicament non-normal consumption.Present invention has found that in the base of the prior art
It on plinth, is added after chlorine residue stabilizer is mixed with corrosion inhibiting and descaling agent, the non-normal consumption of medicament can be further reduced.
3, when recirculated cooling water is containing ammonia nitrogen (for example ammonia factory leakage ammonia, moisturizing are containing ammonia nitrogen, the hydrolysis of nitrogenous medicament or decomposition etc.),
Unless greatly increasing the dosage of chlorine system fungicide, otherwise it is difficult to stablize the contents of residual chlorine in recirculated water in normal controlled level
On.Present invention has found that, even if containing ammonia nitrogen in recirculated cooling water, also can not significantly increased using chlorine residue stabilizer of the invention
Under the premise of chlorination system fungicide dosage, the contents of residual chlorine in recirculated water is stablized in normal controlled level.
4, the prior art sterilize host agent can not microorganism effectively in control loop water when, in order to guarantee to kill microorganism
Effect often adds the technological means of sterilization adjuvant by the way of impact type, large dosage.And preferably for one kind of the invention
Embodiment (continuously adds based on chlorine system fungicide and chlorine residue stabilizer, impact type adds supplemented by non-oxidative antimicrobial),
When microorganism in recirculated water is out of control, it is only necessary to which impact type adds the non-oxidative antimicrobial of low concentration, can effectively solve control and follow
Microorganism in ring water.Further, when non-oxidative antimicrobial is quaternary ammonium salt non-oxidative antimicrobial, the present invention not will lead to
Circulation cooling water system turbidity dramatically increases, therefore is not required to that blowdown is forced to carry out water substitution.It can make circulating water water system
System continuous operation in normal state.
5, when nitrococcus distorted proliferation in recirculated water, the raising of recirculated water Nitrite ion, nitrous be will lead to
Acid ion can destroy chlorine system fungicide, it is caused partly or entirely to fail.In nitrococcus mass propagation, even if large dosage of
Chlorine system fungicide is added, the growth of nitrococcus often also can not be effectively controlled.And for a kind of preferred implementation side of the invention
Formula (continuously adds based on chlorine system fungicide and chlorine residue stabilizer, impact type adds supplemented by quaternary ammonium salt non-oxidative antimicrobial),
The nitrococcus in recirculated water can be made to be effectively controlled.
Other features and advantages of the present invention will the following detailed description will be given in the detailed implementation section.
Specific embodiment
In the context of the present specification, other than the content clearly stated, any matters or item that do not mention are equal
It is directly applicable in those of known in the art without carrying out any change.Moreover, any embodiment described herein can be with
It is freely combined with one or more other embodiments described herein, the technical solution or technical idea being consequently formed are accordingly to be regarded as
A part of the original disclosure of the present invention or original description, and it is not considered as the new content for not disclosing or being expected herein,
Unless those skilled in the art think that the combination is obvious unreasonable.
All features disclosed in this invention can in any combination, these combinations should be understood presently disclosed or note
The content of load, unless those skilled in the art think that the combination is obviously unreasonable.Numerical point disclosed in this specification, is not only wrapped
Specifically disclosed numerical point is included, further includes the endpoint of each numberical range, the range of these numerical point institute any combination should all be regarded
For the present invention range that discloses or has recorded, no matter whether herein separately disclose these numerical value pair.
(1) method stablized the method for chlorine residue and control microorganism
The present invention provides a kind of method of chlorine residue in stable recirculated cooling water, it is included in addition chlorine system in recirculated cooling water
Fungicide, which is characterized in that a effective amount of chlorine residue stabilizer is added into recirculated cooling water, the chlorine residue stabilizer is boiling point
Amine and/or hydramine greater than 100 DEG C.
According to the present invention, in addition to the chlorine residue stabilizer, it is used to stablize the stabilization of halogen and/or chlorine residue without using other
Agent.
The chlorine system fungicide refer in water generate hypochlorite fungicide comprising but be not limited to liquid chlorine,
Sodium hypochlorite, calcium hypochlorite, dichlord isocyanurice acid (one of Puritabs, sym-closene (strong chlorine oil) or it is arbitrary
Combination.In general situation, the dosage of chlorine system fungicide make in recirculated cooling water chlorine residue mass concentration up to 0.5mg/L~
2mg/L, preferably 1mg/L~1.5mg/L.
The chlorine residue stabilizer include but is not limited to the fatty primary monoamine of C5~C10, C2~C10 fatty di-primary amine,
The single secondary amine of fat of C5~C10, the polyethylene polyamine of C4~C10, C5~C10 one of hydramine or its arbitrary combine；
For example it can be selected from di-n-propylamine, amylamine, ethylenediamine, 1,2- propane diamine, 1,3- propane diamine, 1,4- butanediamine, 1,5- pentanediamine, 1,6-
Hexamethylene diamine, diethylenetriamine, triethylene tetramine, tetraethylenepentamine, pentaethylene hexamine, ethanol amine, diethanol amine, triethanolamine,
N, N- dimethylethanolamine, N methyldiethanol amine, N- diethyl ethylene diamine, n-propanolamine, isopropanolamine, diisopropanolamine (DIPA) and
One of triisopropanolamine or its arbitrary combination.
Introduction according to the present invention, in this way it is easy to determine the effective dose of the chlorine residue stabilizer.Generally, chlorine residue stabilizer
Dosage makes chlorine residue stabilizer mass concentration 0.5mg/L~10mg/L, preferably 1mg/L~8mg/L in recirculated cooling water, more preferably
2mg/L~5mg/L.
According to the present invention, when adding chlorine system fungicide and the chlorine residue stabilizer into circulating water water system,
Perhaps the two add the different perhaps the two in position add that the period is different or the two adds position and adds the time
Section is different, to avoid directly contact due to high concentration medicament caused by medicament loss.
According to the present invention, the dosing method of chlorine system fungicide and the chlorine residue stabilizer is continuously to add.
According to the present invention, chlorine residue stabilizer and anti-incrustation corrosion inhibitor are formed into the first mixture, then connects the first mixture
It is continuous to be added in recirculated cooling water.
According to the present invention, the anti-incrustation corrosion inhibitor is commercial goods agent.In first mixture, chlorine residue stabilizer
Shared mass fraction is 0.5%~10%, preferably 1%~8%, further preferred 2%~5%.First mixture
Dosage makes its relative cycle water quality concentration 50mg/L~150mg/L, preferably 80mg/L~120mg/L.
When containing ammonia nitrogen in recirculated cooling water, method of the invention is especially effective.Generally, it is not contained in recirculated cooling water
Ammonia nitrogen, but in some cases, such as ammonia factory leakage ammonia, the hydrolysis that moisturizing is recycle-water, nitrogenous medicament containing ammonia nitrogen or decomposition etc.,
Ammonia nitrogen can be contained in recirculated cooling water, more easily (be greater than in cooperating microorganisms, especially recirculated cooling water containing exceeded at this time
When ammonia nitrogen 10mg/L), situation is more serious.
The present invention also provides a kind of methods of microorganism in control loop cooling water, including are used cooperatively chlorine system fungicide
And non-oxidative antimicrobial, which is characterized in that residual chlorine concentration is stablized using aforementioned any method.
According to the present invention, the dosing method of the non-oxidative antimicrobial adds for impact type.
According to the present invention, the dosage of the non-oxidative antimicrobial make its concentration 2mg/L in recirculated cooling water~
20mg/L, preferably 5mg/L~15mg/L；After adding non oxidizing bactericide, recirculating cooling water system does not force blowdown to carry out water
Body is replaced and continuous operation.
According to the present invention, the non-oxidative antimicrobial includes but is not limited to quaternary ammonium salt non-oxidative antimicrobial, aldehydes sterilization
Agent such as glutaraldehyde, organic tin fungicide, organo bromine microbicide or quaternary phosphonium salt fungicide.
(2) method of heterotroph is controlled
The present invention provides a kind of methods of heterotroph in control loop cooling water, comprising: (1) connects into recirculated cooling water
It is continuous to add chlorine system fungicide and a effective amount of chlorine residue stabilizer, the chlorine residue stabilizer be amine of the boiling point greater than 100 DEG C and/or
Hydramine；(2) when the heterotrophism bacterial content in recirculated cooling water is greater than Con trolling index value, it is non-oxide to add quaternary ammonium salt to impact type
Fungicide.
The step (1) is identical as the corresponding part in aforementioned (one), and details are not described herein by the present invention.
In recirculating cooling water system, the Con trolling index of heterotroph is usually to be not more than 1 × 105A/mL.
According to the present invention, in step (2), the heterotrophism bacterial content in recirculated cooling water is greater than Con trolling index value to control
When between 10 times of index value, quaternary ammonium salt non-oxidative antimicrobial, the quaternary ammonium salt non-oxidative antimicrobial are added to impact type
Dosage make its concentration 2mg/L~20mg/L in recirculated cooling water, preferably 5mg/L~15mg/L；Quaternary ammonium salt is added
After class non oxidizing bactericide, recirculating cooling water system does not force blowdown to carry out water substitution and continuous operation.
According to the present invention, the quaternary ammonium salt non oxidizing bactericide preferably has following structure:
The wherein integer that n is 10~18, preferably 12 or 14；The integer that m is 8~12；X-Selected from Cl-Or Br-。
(3) method of nitrococcus is controlled
The present invention provides a kind of methods of nitrococcus in control loop cooling water, comprising: (1) into recirculated cooling water
Continuously add chlorine system fungicide and a effective amount of chlorine residue stabilizer, the chlorine residue stabilizer be amine of the boiling point greater than 100 DEG C and/
Or hydramine；(2) as the NO in recirculated cooling water2 -When content >=1mg/L, quaternary ammonium salt non-oxidative antimicrobial is added to impact type.
The step (1) and step (2) is identical as the corresponding part in aforementioned (two), and details are not described herein by the present invention.
According to the present invention, in step (2), the NO in recirculated cooling water2 -When content is 1mg/L~3mg/L, impact type
Quaternary ammonium salt non-oxidative antimicrobial is added, the dosage of the quaternary ammonium salt non-oxidative antimicrobial makes it in recirculated cooling water
Concentration is 2mg/L~20mg/L, preferably 5mg/L~15mg/L；After quaternary ammonium salt non oxidizing bactericide is added, recirculated cooling water
System does not force blowdown to carry out water substitution and continuous operation.
The present invention is further illustrated by the following examples.
Various raw materials used in embodiment are conventional substance, can be commercially available.
It tests in the embodiment of the present invention and comparative example and is carried out in dynamic simulation tester, dynamic simulation test method
Chlorine residue analysis method referring to HG/T 2160-2008 " dynamic analogue test of cooling water method ", in dynamic test recirculated cooling water
Referring to the NO in GB/T 14424-2008 " measurement of chlorine residue in industrial circulating cooling water ", dynamic simulation test recirculated cooling water2 -
Analysis method is analyzed referring to GB/T 6912-2008 " measurement of boiler feed water and cooling water analysis method nitrite ", heterotroph
Method is referring to HG/T 4207-2011 " industrial circulating cooling water heterotroph Counting alive microbial plate count ".
Dynamic simulation test test water used is Beijing tap water, and water quality is shown in Table 1.
Table 1
Dynamic simulation test control condition are as follows: 8~10 DEG C of water temperature difference, 0.8~1m/S of water flow velocity of disengaging, cycles of concentration 3.8
(anti-incrustation corrosion inhibitor II is by Beijing Lin Hua water treatment agent factory according to HG/ by~4.2, II 90~110mg/L of mass concentration of anti-incrustation corrosion inhibitor
T 2430-2009 production).
Embodiment 1
It weighs 2g ethylenediamine addition 98g anti-incrustation corrosion inhibitor II and obtains the first mixture, it is mixed to be made into first with Beijing tap water
Conjunction object content is moisturizing of the solution of 25mg/L as dynamic model；The sym-closene of effective chlorine 85% has been made into deionized water
The oxidizing bactericide mother liquor for imitating chlorine 1mg/mL, is added continuously in dynamic model tower basin with constant flow pump with 1mL/min flow velocity；3rd day
Up to after cycles of concentration, daily sampling analysis chlorine residue, test result is shown in Table 2.
Embodiment 2
It weighs 3g ethanol amine addition 97g anti-incrustation corrosion inhibitor II and obtains the first mixture, it is mixed to be made into first with Beijing tap water
The solution that object content is 25mg/L is closed, then 2.5mg/L NH is added into this solution4 +Moisturizing as dynamic model；Effective chlorine 10%
NaClO is made into the oxidizing bactericide mother liquor of effective chlorine 1mg/mL with deionized water, is continuously added with constant flow pump with 1mL/min flow velocity
Enter into dynamic model tower basin；After 3rd day reaches cycles of concentration, daily sampling analysis chlorine residue, test result is shown in Table 2.
Embodiment 3
It weighs 5g triethylene tetramine 95g anti-incrustation corrosion inhibitor II is added and obtain the first mixture, be made into the with Beijing tap water
One mixture content is the solution of 25mg/L, then 2.5mg/L NH is added into this solution4 +Moisturizing as dynamic model；Effective chlorine
65% dichlord isocyanurice acid is made into the oxidizing bactericide mother liquor of effective chlorine 1mg/mL with deionized water, with constant flow pump with 1mL/
Min flow velocity is added continuously in dynamic model tower basin；After 3rd day reaches cycles of concentration, daily sampling analysis chlorine residue, test result is shown in Table 2.
Embodiment 4
It weighs 0.2g di-n-propylamine 98.8g anti-incrustation corrosion inhibitor II is added and obtain the first mixture, be made into the with Beijing tap water
One mixture content is moisturizing of the solution of 25mg/L as dynamic model；The NaClO of effective chlorine 10% is made into effectively with deionized water
The oxidizing bactericide mother liquor of chlorine 1mg/mL is added continuously in dynamic model tower basin with constant flow pump with 1mL/min flow velocity；It reaches within 3rd day
After cycles of concentration, daily sampling analysis chlorine residue, test result is shown in Table 2.
Embodiment 5
It weighs 12g isopropanolamine addition 88g anti-incrustation corrosion inhibitor II and obtains the first mixture, be made into first with Beijing tap water
Mixture content is moisturizing of the solution of 25mg/L as dynamic model；The dichlord isocyanurice acid of effective chlorine 65% is made into deionized water
The oxidizing bactericide mother liquor of effective chlorine 1mg/mL is added continuously in dynamic model tower basin with constant flow pump with 1mL/min flow velocity；3rd
After it reaches cycles of concentration, daily sampling analysis chlorine residue, test result is shown in Table 2.
Comparative example 1
Beijing tap water is used to be made into the solution of 25mg/L as the moisturizing of dynamic model anti-incrustation corrosion inhibitor II；Effective chlorine 10%
NaClO is made into the oxidizing bactericide mother liquor of effective chlorine 1mg/mL with deionized water, is continuously added with constant flow pump with 1mL/min flow velocity
Enter into dynamic model tower basin；After 3rd day reaches cycles of concentration, daily sampling analysis chlorine residue, test result is shown in Table 2.
Comparative example 2
Anti-incrustation corrosion inhibitor II is made into the solution of 25mg/L with Beijing tap water, then 2.5mg/L is added into this solution
NH4 +Moisturizing as dynamic model；The NaClO of effective chlorine 10% is made into the oxidizing bactericide mother of effective chlorine 1mg/mL with deionized water
Liquid is added continuously in dynamic model tower basin with constant flow pump with 1mL/min flow velocity；After 3rd day reaches cycles of concentration, more than daily sampling analysis
Chlorine, test result are shown in Table 2.
Comparative example 3
Anti-incrustation corrosion inhibitor II is made into the solution of 25mg/L with Beijing tap water, then 2.5mg/L is added into this solution
NH4 +Moisturizing as dynamic model；The NaClO of effective chlorine 10% is made into the oxidizing bactericide mother of effective chlorine 1mg/mL with deionized water
Liquid is added continuously in dynamic model tower basin with constant flow pump with 2mL/min flow velocity；After 3rd day reaches cycles of concentration, more than daily sampling analysis
Chlorine, test result are shown in Table 2.
Comparative example 4
Anti-incrustation corrosion inhibitor II is made into the solution of 25mg/L with Beijing tap water, then 2.5mg/L is added into this solution
NH4 +Moisturizing as dynamic model；The NaClO of effective chlorine 10% is made into the oxidizing bactericide mother of effective chlorine 4mg/mL with deionized water
Liquid is added continuously in dynamic model tower basin with constant flow pump with 4mL/min flow velocity；After 3rd day reaches cycles of concentration, more than daily sampling analysis
Chlorine, test result are shown in Table 2.
Table 2
The test result of table 2 shows:
(1) comparative example 1, the residual chlorine amount of comparative example 2 that chlorine residue stabilizer is not added are low, only 0~0.3mg/L.
(2) it is not added the comparative example 3 of chlorine residue stabilizer, the dosage of fungicide containing oxychloride increases by 1 times, and chlorine residue is 0.4~
0.6mg/L。
(3) it is not added the comparative example 4 of chlorine residue stabilizer, the dosage of fungicide containing oxychloride increases to 4 times, and chlorine residue is 1.1~
1.5mg/L is suitable with Examples 1 to 3 and 5 chlorine residue of embodiment.
(4) chlorine residue consistent dose added by embodiment 4 is low, and chlorine residue is lower.
(5) chlorine residue consistent dose added by embodiment 5 is high, and chlorine residue is suitable with Examples 1 to 3 chlorine residue, but chlorine residue stabilizer adds
Amount is big, increased costs.
Embodiment 6
It weighs 2g ethylenediamine addition 98g anti-incrustation corrosion inhibitor II and obtains the first mixture, it is mixed to be made into first with Beijing tap water
The solution that object content is 25mg/L is closed, then 2.5mg/L NH is added into this solution4 +Moisturizing as dynamic model；Effective chlorine 85%
Sym-closene is made into the oxidizing bactericide mother liquor of effective chlorine 1mg/mL with deionized water, is flowed with constant flow pump with 1mL/min
Speed is added continuously in dynamic model tower basin；After dynamic model continuous operation 15 days, after sampling analysis chlorine residue and heterotroph, then impact is added
15mg/L dodecyl benzyl dimethyl ammonium chloride；It continues to run, daily sampling analysis chlorine residue and heterotroph, test result are shown in Table
3。
Embodiment 7
It weighs 3g ethanol amine addition 97g anti-incrustation corrosion inhibitor II and obtains the first mixture, it is mixed to be made into first with Beijing tap water
The solution that object content is 25mg/L is closed, then 2.5mg/L NH is added into this solution4 +Moisturizing as dynamic model；Effective chlorine 10%
NaClO is made into the oxidizing bactericide mother liquor of effective chlorine 1mg/mL with deionized water, is continuously added with constant flow pump with 1mL/min flow velocity
Enter into dynamic model tower basin；After dynamic model continuous operation 15 days, after sampling analysis chlorine residue and heterotroph, then 10mg/L ten is added in impact
Tetraalkyl dimethyl benzyl ammonium chloride；It continues to run, daily sampling analysis chlorine residue and heterotroph, test result are shown in Table 3.
Embodiment 8
It weighs 5g triethylene tetramine 95g anti-incrustation corrosion inhibitor II is added and obtain the first mixture, be made into the with Beijing tap water
One mixture content is the solution of 25mg/L, then 2.5mg/L NH is added into this solution4 +Moisturizing as dynamic model；Effective chlorine
65% dichlord isocyanurice acid is made into the oxidizing bactericide mother liquor of effective chlorine 1mg/mL with deionized water, with constant flow pump with 1mL/
Min flow velocity is added continuously in dynamic model tower basin；After dynamic model continuous operation 15 days, after sampling analysis chlorine residue and heterotroph, then impact
Property be added the bis- dodecyl dimethyl ammonium chlorides of 5mg/L；It continues to run, daily sampling analysis chlorine residue and heterotroph, test result
It is shown in Table 3.
Embodiment 9
It weighs 0.2g di-n-propylamine 98.8g anti-incrustation corrosion inhibitor II is added and obtain the first mixture, be made into the with Beijing tap water
One mixture content is the solution of 25mg/L, then 2.5mg/L NH is added into this solution4 +Moisturizing as dynamic model；Effective chlorine
10% NaClO is made into the oxidizing bactericide mother liquor of effective chlorine 1mg/mL with deionized water, with constant flow pump with 1mL/min flow velocity
It is added continuously in dynamic model tower basin；After dynamic model continuous operation 15 days, after sampling analysis chlorine residue and heterotroph, then impact is added
10mg/L myristyl benzyl dimethyl ammonium chloride；It continues to run, daily sampling analysis chlorine residue and heterotroph, test result are shown in Table
3。
Embodiment 10
It weighs 12g isopropanolamine addition 88g anti-incrustation corrosion inhibitor II and obtains the first mixture, be made into first with Beijing tap water
Mixture content is the solution of 25mg/L, then 2.5mg/L NH is added into this solution4 +Moisturizing as dynamic model；Effective chlorine 65%
Dichlord isocyanurice acid the oxidizing bactericide mother liquor of effective chlorine 1mg/mL is made into deionized water, with constant flow pump with 1mL/min
Flow velocity is added continuously in dynamic model tower basin；After dynamic model continuous operation 15 days, after sampling analysis chlorine residue and heterotroph, then impact adds
Enter the bis- dodecyl dimethyl ammonium chlorides of 5mg/L；It continues to run, daily sampling analysis chlorine residue and heterotroph, test result are shown in Table
3。
Comparative example 5
Anti-incrustation corrosion inhibitor II is made into the solution of 25mg/L with Beijing tap water, then 2.5mg/L is added into this solution
NH4 +Moisturizing as dynamic model；The NaClO of effective chlorine 10% is made into the oxidizing bactericide mother of effective chlorine 1mg/mL with deionized water
Liquid is added continuously in dynamic model tower basin with constant flow pump with 1mL/min flow velocity；After dynamic model continuous operation 15 days, sampling analysis chlorine residue
After heterotroph；It continues to run, daily sampling analysis chlorine residue and heterotroph, test result are shown in Table 3.
Comparative example 6
Anti-incrustation corrosion inhibitor II is made into the solution of 25mg/L with Beijing tap water, then 2.5mg/L is added into this solution
NH4 +Moisturizing as dynamic model；The NaClO of effective chlorine 10% is made into the oxidizing bactericide mother of effective chlorine 1mg/mL with deionized water
Liquid is added continuously in dynamic model tower basin with constant flow pump with 1mL/min flow velocity；After dynamic model continuous operation 15 days, sampling analysis chlorine residue
After heterotroph, then 10mg/L myristyl benzyl dimethyl ammonium chloride is added in impact；It continues to run, more than daily sampling analysis
Chlorine and heterotroph, test result are shown in Table 3.
Embodiment 11
It weighs 3g ethanol amine addition 97g anti-incrustation corrosion inhibitor II and obtains the first mixture, it is mixed to be made into first with Beijing tap water
The solution that object content is 25mg/L is closed, then 2.5mg/L NH is added into this solution4 +Moisturizing as dynamic model；Effective chlorine 10%
NaClO is made into the oxidizing bactericide mother liquor of effective chlorine 1mg/mL with deionized water, is continuously added with constant flow pump with 1mL/min flow velocity
Enter into dynamic model tower basin；After dynamic model continuous operation 15 days, after sampling analysis chlorine residue and heterotroph；It continues to run, daily sampling point
Analysis chlorine residue and heterotroph, test result are shown in Table 3.
Embodiment 12
It weighs 3g ethanol amine addition 97g anti-incrustation corrosion inhibitor II and obtains the first mixture, it is mixed to be made into first with Beijing tap water
Conjunction object content is moisturizing of the solution of 25mg/L as dynamic model；The NaClO of effective chlorine 10% is made into effective chlorine with deionized water
The oxidizing bactericide mother liquor of 1mg/mL is added continuously in dynamic model tower basin with constant flow pump with 1mL/min flow velocity；Dynamic model is continuously transported
After row 15 days, sampling analysis chlorine residue and heterotroph, test result are shown in Table 3.
Table 3
The test result of table 3 shows:
(1) chlorine residue stabilizer is not added, the comparative example 5 that is not added quaternary ammonium salt does not measure chlorine residue, number of heterotrophic bacteria grade up to 7 powers,
Microorganism is far more than 1 × 105The Con trolling index of a/mL.
(2) 6 residual chlorine amount of comparative example that chlorine residue stabilizer plus quaternary ammonium salt is not added is low, and only 0.1~0.3mg/L, adds quaternary ammonium salt
Afterwards, number of heterotrophic bacteria grade is down to 6 powers from 7 powers, but microorganism is still above 1 × 105The Con trolling index of a/mL.
(3) the 11 0.6~0.7mg/L of chlorine residue of embodiment for adding chlorine residue stabilizer, quaternary ammonium salt being not added, microorganism is more than 1 × 105
The Con trolling index of a/mL.
(4) plus the 15th day 0.6~0.8mg/L of chlorine residue in embodiment 6~8 of chlorine residue stabilizer plus quaternary ammonium salt, microorganism are super
Cross 1 × 105The Con trolling index of a/mL, but number of heterotrophic bacteria grade after quaternary ammonium salt is added from 5 powers to be down to 3 powers, control of microorganisms reaches
Mark.
(5) embodiment 9 plus a small amount of chlorine residue stabilizer, even if plus quaternary ammonium salt, control of microorganisms it is also not up to standard.
(6) 10 increasing amount chlorine residue stabilizer of embodiment, the 15th day microorganism is exceeded, adds number of heterotrophic bacteria grade after quaternary ammonium salt
Also 3 powers are down to from 5 powers, control of microorganisms is up to standard, but chlorine residue stabilizer dosage is big, reaches identical control of microorganisms effect
Under, increased costs.
Embodiment 13
It weighs 2g ethylenediamine addition 98g anti-incrustation corrosion inhibitor II and obtains the first mixture, it is mixed to be made into first with Beijing tap water
The solution that object content is 25mg/L is closed, then 2.5mg/L NH is added into this solution4 +Moisturizing as dynamic model；Effective chlorine 85%
Sym-closene is made into the oxidizing bactericide mother liquor of effective chlorine 1mg/mL with deionized water, is flowed with constant flow pump with 1mL/min
Speed is added continuously in dynamic model tower basin；After dynamic model continuous operation 15 days, sampling analysis NO2 -, chlorine residue, after nitrococcus, then impact
Property be added 15mg/L dodecyl benzyl dimethyl ammonium chloride；It continues to run, daily sampling analysis NO2 -, chlorine residue, nitrococcus,
Test result is shown in Table 4.
Embodiment 14
It weighs 3g ethanol amine addition 97g anti-incrustation corrosion inhibitor II and obtains the first mixture, it is mixed to be made into first with Beijing tap water
The solution that object content is 25mg/L is closed, then 2.5mg/L NH is added in this solution4 +Moisturizing as dynamic model；Effective chlorine 10%
NaClO is made into the oxidizing bactericide mother liquor of effective chlorine 1mg/mL with deionized water, is continuously added with constant flow pump with 1mL/min flow velocity
Enter into dynamic model tower basin；After dynamic model continuous operation 15 days, sampling analysis NO2 -, chlorine residue, after nitrococcus, then impact is added
10mg/L myristyl benzyl dimethyl ammonium chloride；It continues to run, daily sampling analysis NO2 -, chlorine residue, nitrococcus, as a result see
Table 2.
Embodiment 15
It weighs 5g triethylene tetramine 95g anti-incrustation corrosion inhibitor II is added and obtain the first mixture, be made into the with Beijing tap water
One mixture content is the solution of 25mg/L, then 2.5mg/L NH is added into this solution4 +Moisturizing as dynamic model；Effective chlorine
65% dichlord isocyanurice acid is made into the oxidizing bactericide mother liquor of effective chlorine 1mg/mL with deionized water, with constant flow pump with 1mL/
Min flow velocity is added continuously in dynamic model tower basin；After dynamic model continuous operation 15 days, sampling analysis NO2 -, chlorine residue, after nitrococcus, then
The bis- dodecyl dimethyl ammonium chlorides of 5mg/L are added in impact；It continues to run, daily sampling analysis NO2 -, chlorine residue, nitrococcus,
Test result is shown in Table 4.
Embodiment 16
It weighs 0.2g di-n-propylamine 98.8g anti-incrustation corrosion inhibitor II is added and obtain the first mixture, be made into the with Beijing tap water
One mixture content is the solution of 25mg/L, then 2.5mg/L NH is added into this solution4 +Moisturizing as dynamic model；Effective chlorine
10% NaClO is made into the oxidizing bactericide mother liquor of effective chlorine 1mg/mL with deionized water, with constant flow pump with 1mL/min flow velocity
It is added continuously in dynamic model tower basin；After dynamic model continuous operation 15 days, sampling analysis NO2 -, chlorine residue, after nitrococcus, then impact
10mg/L myristyl benzyl dimethyl ammonium chloride is added；It continues to run, daily sampling analysis NO2 -, chlorine residue, nitrococcus, examination
It tests and the results are shown in Table 4.
Embodiment 17
It weighs 12g isopropanolamine addition 88g anti-incrustation corrosion inhibitor II and obtains the first mixture, be made into first with Beijing tap water
Mixture content is the solution of 25mg/L, then 2.5mg/L NH is added into this solution4 +Moisturizing as dynamic model；Effective chlorine 65%
Dichlord isocyanurice acid the oxidizing bactericide mother liquor of effective chlorine 1mg/mL is made into deionized water, with constant flow pump with 1mL/min
Flow velocity is added continuously in dynamic model tower basin；After dynamic model continuous operation 15 days, sampling analysis NO2 -, chlorine residue, after nitrococcus, then rush
The bis- dodecyl dimethyl ammonium chlorides of 5mg/L are added in hitting property；It continues to run, daily sampling analysis NO2 -, chlorine residue, nitrococcus, examination
It tests and the results are shown in Table 4.
Comparative example 7
Anti-incrustation corrosion inhibitor II is made into the solution of 25mg/L with Beijing tap water, then 2.5mg/L is added into this solution
NH4 +Moisturizing as dynamic model；The NaClO of effective chlorine 10% is made into the oxidizing bactericide mother of effective chlorine 1mg/mL with deionized water
Liquid is added continuously in dynamic model tower basin with constant flow pump with 1mL/min flow velocity；After dynamic model continuous operation 15 days, sampling analysis NO2 -、
After chlorine residue, nitrococcus；It continues to run, daily sampling analysis NO2 -, chlorine residue, nitrococcus, test result is shown in Table 4.
Comparative example 8
Anti-incrustation corrosion inhibitor II is made into the solution of 25mg/L with Beijing tap water, then 2.5mg/L is added into this solution
NH4 +Moisturizing as dynamic model；The NaClO of effective chlorine 10% is made into the oxidizing bactericide mother of effective chlorine 1mg/mL with deionized water
Liquid is added continuously in dynamic model tower basin with constant flow pump with 1mL/min flow velocity；After dynamic model continuous operation 15 days, sampling analysis NO2 -、
After chlorine residue, nitrococcus, adds impact and 10mg/L myristyl benzyl dimethyl ammonium chloride is added；It continues to run, daily
Sampling analysis NO2 -, chlorine residue, nitrococcus, test result is shown in Table 4.
Embodiment 18
It weighs 3g ethanol amine addition 97g anti-incrustation corrosion inhibitor II and obtains the first mixture, it is mixed to be made into first with Beijing tap water
The solution that object content is 25mg/L is closed, then 2.5mg/L NH is added into this solution4 +Moisturizing as dynamic model；Effective chlorine 10%
NaClO is made into the oxidizing bactericide mother liquor of effective chlorine 1mg/mL with deionized water, is continuously added with constant flow pump with 1mL/min flow velocity
Enter into dynamic model tower basin；After dynamic model continuous operation 15 days, sampling analysis NO2 -, chlorine residue, after nitrococcus；It continues to run, takes daily
Sample analyzes NO2 -, chlorine residue, nitrococcus, coupon results are shown in Table 4.
Comparative example 9
Anti-incrustation corrosion inhibitor II is made into the solution of 25mg/L with Beijing tap water, then 2.5mg/L is added into this solution
NH4 +Moisturizing as dynamic model；The NaClO of effective chlorine 10% is made into the oxidizing bactericide mother of effective chlorine 1mg/mL with deionized water
Liquid is added continuously in dynamic model tower basin with constant flow pump with 1mL/min flow velocity；After dynamic model continuous operation 15 days, sampling analysis NO2 -、
After chlorine residue, nitrococcus, stops plus the chlorination of 100mg/L myristyl benzyl dimethyl is added in NaClO oxidizing bactericide, impact
Ammonium；It continues to run, daily sampling analysis NO2 -, chlorine residue, nitrococcus, test result is shown in Table 4.
Comparative example 10
Anti-incrustation corrosion inhibitor II is made into the solution of 25mg/L with Beijing tap water, then 2.5mg/L is added into this solution
NH4 +Moisturizing as dynamic model；The NaClO of effective chlorine 10% is made into the oxidizing bactericide mother of effective chlorine 1mg/mL with deionized water
Liquid is added continuously in dynamic model tower basin with constant flow pump with 1mL/min flow velocity；After dynamic model continuous operation 15 days, sampling analysis NO2 -、
After chlorine residue, nitrococcus, stops plus the chlorination of 150mg/L myristyl benzyl dimethyl is added in NaClO oxidizing bactericide, impact
Ammonium；It continues to run, daily sampling analysis NO2 -, chlorine residue, nitrococcus, test result is shown in Table 4.
Table 4
Table 4 the result shows that:
(1) comparative example 7 that chlorine residue stabilizer is not added, quaternary ammonium salt is not added, the nitrococcus order of magnitude are constant.
(2) comparative example 8 of chlorine residue stabilizer plus quaternary ammonium salt is not added, 1 order of magnitude only drops in nitrococcus.
(3) plus chlorine residue stabilizer, the embodiment 18 that quaternary ammonium salt is not added, the nitrococcus order of magnitude are constant.
Stop after (4) the 15th days plus 100mg/L myristyl benzyl dimethyl is added in NaClO oxidizing bactericide, impact
The comparative example 9 of ammonium chloride, nitrococcus are down to the 2 power orders of magnitude from the 5 power orders of magnitude, and nitrococcus quantity is still higher than embodiment
1~3 and embodiment 5.In addition, turbidity of circulating water reaches 42mg/L, it has been more than that control of the turbidity of circulating water no more than 20mg/L refers to
Mark needs to force blowdown replacement cycles water water body, and operating cost increases.
Stop after (5) the 15th days plus 150mg/L myristyl benzyl dimethyl is added in NaClO oxidizing bactericide, impact
The comparative example 10 of ammonium chloride, nitrococcus are all killed.But foam is more in recirculated water, defoaming agent need to be added to control foam, and follow
Ring water turbidity reaches 66mg/L, has been more than the Con trolling index that turbidity of circulating water is not more than 20mg/L, needs that blowdown displacement is forced to follow
Ring water water body, operating cost increase.
Test case
The NaClO for taking 100g effective chlorine 10% adds 20g deionized water to be uniformly mixed, and survey chlorine residue is 8.2mg/L；Separately take
The NaClO of 100g effective chlorine 10% adds 20g ethanol amine to be uniformly mixed, and survey chlorine residue is 6.8mg/L, effective chlorine loss 17.1%.
Claims (7)
1. a kind of method of heterotroph in control loop cooling water, comprising: (1) continuously add the sterilization of chlorine system into recirculated cooling water
Agent and a effective amount of chlorine residue stabilizer, the chlorine residue stabilizer are the amine and/or hydramine that boiling point is greater than 100 DEG C；(2) work as circulation
When heterotrophism bacterial content in cooling water is greater than Con trolling index value, quaternary ammonium salt non-oxidative antimicrobial is added to impact type；
Wherein, chlorine residue stabilizer and anti-incrustation corrosion inhibitor are formed into the first mixture, then is continuously added to recycle by the first mixture
In cooling water；In first mixture, mass fraction shared by chlorine residue stabilizer is 0.5%~10%；First mixing
The dosage of object makes its relative cycle water quality concentration 50mg/L~150mg/L；The chlorine residue stabilizer be selected from di-n-propylamine,
Amylamine, ethylenediamine, 1,2- propane diamine, 1,3- propane diamine, 1,4- butanediamine, 1,5- pentanediamine, 1,6- hexamethylene diamine, divinyl three
Amine, triethylene tetramine, tetraethylenepentamine, pentaethylene hexamine, ethanol amine, diethanol amine, triethanolamine, N, N- dimethyl ethanol
In amine, N methyldiethanol amine, N- diethyl ethylene diamine, n-propanolamine, isopropanolamine, diisopropanolamine (DIPA) and triisopropanolamine
A kind of or its arbitrary combination.
2. the method according to claim 1, wherein chlorine system fungicide is being recycled with the chlorine residue stabilizer
Position difference is added in cooling water system.
3. the method according to claim 1, wherein chlorine system fungicide is selected from liquid chlorine, sodium hypochlorite, secondary
One of calcium chlorate, dichlord isocyanurice acid, sym-closene or its arbitrary combination.
4. the method according to claim 1, wherein the dosage of chlorine system fungicide makes in recirculated cooling water
Chlorine residue mass concentration reaches 0.5mg/L~2mg/L.
5. the method according to claim 1, wherein containing or not contain ammonia nitrogen in the recirculated cooling water.
6. the method according to claim 1, wherein the heterotrophism bacterial content in step (2), in recirculated cooling water
When between 10 times greater than Con trolling index value to Con trolling index value, quaternary ammonium salt non-oxidative antimicrobial, institute are added to impact type
State concentration 2mg/L~20mg/L that the dosage of quaternary ammonium salt non-oxidative antimicrobial makes it in recirculated cooling water；Season is added
After ammonium salt class non oxidizing bactericide, recirculating cooling water system does not force blowdown to carry out water substitution and continuous operation.
7. the method according to claim 1, wherein the quaternary ammonium salt non oxidizing bactericide has as follows
Structure:
The wherein integer that n is 10~18；The integer that m is 8~12；X-Selected from Cl-Or Br-。
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Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP0051967A1 (en) * | 1980-10-30 | 1982-05-19 | Uss Engineers And Consultants, Inc. | Chlorination of wastewater |
| CN1417139A (en) * | 2001-11-08 | 2003-05-14 | 北京燕山石油化工公司研究院 | Method for reusing ammonia nitrogen containing effluent as circular cooling water |
| CN1699204A (en) * | 2005-06-07 | 2005-11-23 | 南开大学 | Control technology for tubificidae in tap water |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20040084383A1 (en) * | 2002-10-30 | 2004-05-06 | Buckman Laboratories International, Inc. | Method to inhibit growth of microorganisms in aqueous systems and on substrates using a persulfate and a bromide |
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2015
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Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP0051967A1 (en) * | 1980-10-30 | 1982-05-19 | Uss Engineers And Consultants, Inc. | Chlorination of wastewater |
| CN1417139A (en) * | 2001-11-08 | 2003-05-14 | 北京燕山石油化工公司研究院 | Method for reusing ammonia nitrogen containing effluent as circular cooling water |
| CN1699204A (en) * | 2005-06-07 | 2005-11-23 | 南开大学 | Control technology for tubificidae in tap water |
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