CN105417789B - A kind of method for removing Measures of Algae in Water Body - Google Patents
A kind of method for removing Measures of Algae in Water Body Download PDFInfo
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- CN105417789B CN105417789B CN201511015325.8A CN201511015325A CN105417789B CN 105417789 B CN105417789 B CN 105417789B CN 201511015325 A CN201511015325 A CN 201511015325A CN 105417789 B CN105417789 B CN 105417789B
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 108
- 241000195493 Cryptophyta Species 0.000 title claims abstract description 99
- 238000000034 method Methods 0.000 title claims abstract description 17
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 claims abstract description 38
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims abstract description 28
- LHJQIRIGXXHNLA-UHFFFAOYSA-N calcium peroxide Chemical compound [Ca+2].[O-][O-] LHJQIRIGXXHNLA-UHFFFAOYSA-N 0.000 claims abstract description 22
- 229910000019 calcium carbonate Inorganic materials 0.000 claims abstract description 19
- 239000000843 powder Substances 0.000 claims abstract description 15
- GNTDGMZSJNCJKK-UHFFFAOYSA-N divanadium pentaoxide Chemical compound O=[V](=O)O[V](=O)=O GNTDGMZSJNCJKK-UHFFFAOYSA-N 0.000 claims abstract description 14
- 239000002245 particle Substances 0.000 claims abstract description 14
- ZKQDCIXGCQPQNV-UHFFFAOYSA-N Calcium hypochlorite Chemical compound [Ca+2].Cl[O-].Cl[O-] ZKQDCIXGCQPQNV-UHFFFAOYSA-N 0.000 claims abstract description 13
- 239000007844 bleaching agent Substances 0.000 claims abstract description 13
- 239000004343 Calcium peroxide Substances 0.000 claims abstract description 11
- 235000019402 calcium peroxide Nutrition 0.000 claims abstract description 11
- 230000003647 oxidation Effects 0.000 claims abstract description 8
- 238000007254 oxidation reaction Methods 0.000 claims abstract description 8
- 230000001954 sterilising effect Effects 0.000 claims abstract description 8
- 238000003756 stirring Methods 0.000 claims description 46
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims description 24
- 238000006243 chemical reaction Methods 0.000 claims description 23
- 230000004044 response Effects 0.000 claims description 12
- ONCZQWJXONKSMM-UHFFFAOYSA-N dialuminum;disodium;oxygen(2-);silicon(4+);hydrate Chemical compound O.[O-2].[O-2].[O-2].[O-2].[O-2].[O-2].[O-2].[O-2].[O-2].[O-2].[O-2].[O-2].[Na+].[Na+].[Al+3].[Al+3].[Si+4].[Si+4].[Si+4].[Si+4] ONCZQWJXONKSMM-UHFFFAOYSA-N 0.000 claims description 10
- 238000000227 grinding Methods 0.000 claims description 10
- 229940080314 sodium bentonite Drugs 0.000 claims description 10
- 229910000280 sodium bentonite Inorganic materials 0.000 claims description 10
- 239000000203 mixture Substances 0.000 claims description 7
- 230000005251 gamma ray Effects 0.000 claims description 6
- 239000007788 liquid Substances 0.000 claims description 6
- 230000001590 oxidative effect Effects 0.000 claims description 6
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 claims description 4
- 239000011575 calcium Substances 0.000 claims description 4
- 229910052791 calcium Inorganic materials 0.000 claims description 4
- 230000001678 irradiating effect Effects 0.000 claims description 4
- 238000005516 engineering process Methods 0.000 claims description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims 1
- 229910052799 carbon Inorganic materials 0.000 claims 1
- 230000000694 effects Effects 0.000 abstract description 7
- 238000003672 processing method Methods 0.000 abstract description 7
- 230000034994 death Effects 0.000 abstract description 6
- 231100000517 death Toxicity 0.000 abstract description 6
- 230000006872 improvement Effects 0.000 abstract description 5
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 4
- 239000001301 oxygen Substances 0.000 abstract description 4
- 229910052760 oxygen Inorganic materials 0.000 abstract description 4
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 abstract description 2
- 239000000920 calcium hydroxide Substances 0.000 abstract description 2
- 229910001861 calcium hydroxide Inorganic materials 0.000 abstract description 2
- 230000009286 beneficial effect Effects 0.000 abstract 1
- 210000000170 cell membrane Anatomy 0.000 abstract 1
- 230000006378 damage Effects 0.000 description 6
- 239000000126 substance Substances 0.000 description 5
- 241000192700 Cyanobacteria Species 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 239000003053 toxin Substances 0.000 description 4
- 231100000765 toxin Toxicity 0.000 description 4
- 108700012359 toxins Proteins 0.000 description 4
- 244000005700 microbiome Species 0.000 description 3
- 241000251468 Actinopterygii Species 0.000 description 2
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 2
- 239000003619 algicide Substances 0.000 description 2
- 230000008859 change Effects 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 238000012851 eutrophication Methods 0.000 description 2
- 239000007789 gas Substances 0.000 description 2
- 239000012535 impurity Substances 0.000 description 2
- 150000002978 peroxides Chemical class 0.000 description 2
- 230000009467 reduction Effects 0.000 description 2
- 239000011734 sodium Substances 0.000 description 2
- 229910052708 sodium Inorganic materials 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- DTGKSKDOIYIVQL-WEDXCCLWSA-N (+)-borneol Chemical compound C1C[C@@]2(C)[C@@H](O)C[C@@H]1C2(C)C DTGKSKDOIYIVQL-WEDXCCLWSA-N 0.000 description 1
- REPVLJRCJUVQFA-UHFFFAOYSA-N (-)-isopinocampheol Natural products C1C(O)C(C)C2C(C)(C)C1C2 REPVLJRCJUVQFA-UHFFFAOYSA-N 0.000 description 1
- 206010003497 Asphyxia Diseases 0.000 description 1
- 208000005623 Carcinogenesis Diseases 0.000 description 1
- 239000005749 Copper compound Substances 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- 108090000790 Enzymes Proteins 0.000 description 1
- 102000004190 Enzymes Human genes 0.000 description 1
- 208000027418 Wounds and injury Diseases 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 238000011001 backwashing Methods 0.000 description 1
- 230000008901 benefit Effects 0.000 description 1
- 239000003124 biologic agent Substances 0.000 description 1
- 229940116229 borneol Drugs 0.000 description 1
- CKDOCTFBFTVPSN-UHFFFAOYSA-N borneol Natural products C1CC2(C)C(C)CC1C2(C)C CKDOCTFBFTVPSN-UHFFFAOYSA-N 0.000 description 1
- 230000036952 cancer formation Effects 0.000 description 1
- 231100000504 carcinogenesis Toxicity 0.000 description 1
- 239000004927 clay Substances 0.000 description 1
- 150000001879 copper Chemical class 0.000 description 1
- 150000001880 copper compounds Chemical class 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- DTGKSKDOIYIVQL-UHFFFAOYSA-N dl-isoborneol Natural products C1CC2(C)C(O)CC1C2(C)C DTGKSKDOIYIVQL-UHFFFAOYSA-N 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 231100000206 health hazard Toxicity 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- 231100000405 induce cancer Toxicity 0.000 description 1
- 208000014674 injury Diseases 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 230000000149 penetrating effect Effects 0.000 description 1
- 230000000505 pernicious effect Effects 0.000 description 1
- 230000029553 photosynthesis Effects 0.000 description 1
- 238000010672 photosynthesis Methods 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 229910052720 vanadium Inorganic materials 0.000 description 1
- LEONUFNNVUYDNQ-UHFFFAOYSA-N vanadium atom Chemical compound [V] LEONUFNNVUYDNQ-UHFFFAOYSA-N 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- 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
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/307—Treatment of water, waste water, or sewage by irradiation with X-rays or gamma radiation
-
- 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
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/32—Treatment of water, waste water, or sewage by irradiation with ultraviolet light
-
- 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
- C02F1/50—Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
-
- 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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
- C02F2301/08—Multistage treatments, e.g. repetition of the same process step under different conditions
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Catching Or Destruction (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Agricultural Chemicals And Associated Chemicals (AREA)
Abstract
The invention discloses a kind of method for removing Measures of Algae in Water Body, belong to water body treating technical field.The present invention carries out pre-oxidation treatment by adding vanadic anhydride in algae pollution water body, then adds calcium carbonate powder and hydrochloric acid, produces substantial amounts of CO2And heat, the cell membrane of algae is promoted to open, calper calcium peroxide is added again, produce the death that substantial amounts of oxygen promotes algae, the calcium hydroxide of generation is used to adjust water pH value, and algae is settled down in water, then by adding particle made from polyvinylamine, promote algae to lose activity, be thoroughly dead, being eventually adding the processing procedure that bleaching powder carries out sterilizing to water body.The beneficial effects of the invention are as follows：Processing method of the present invention is quick, and more than 99.8% is up to algae removal rate；To water body non-secondary pollution after processing, suitable for large area, the improvement of sudden algal tufa.
Description
Technical field
The present invention relates to a kind of method for removing Measures of Algae in Water Body, belong to water body treating technical field.
Background technology
In recent years, China's water body is in eutrophication, and weight eutrophy and supereutrophic are serious, so as to result in algae
Class wawter bloom phenomenon frequently occurs.The harm performance of algae is mainly the undue growth of algae in water, water body color is changed,
Landscape function is lost；Substantial amounts of algae is overlying on the water surface, blocks the photosynthesis of plants in water, causes water body severe depletion of oxygen, together
When the dead process consumption oxygen in water decomposed of algae, make the deaths by suffocation such as fish, the ecological functions of heavy damage water body；Algae
The materials such as the ground depth and the different borneol of 2- methyl that are discharged in class growth course cause running water peculiar smell, have a strong impact on the mouth of running water
Sense, while the Algae toxins of algae release can not be removed by the water technology of routine, and Algae toxins may induce cancer, to making
The health hazard of user is very big；Algae in raw water of waterworks can block filter tank, cause water factory's filter back washing frequency rise,
So as to lift water producing cost, water supply quality can be influenceed by penetrating the algae in filter tank on a small quantity.
Removing the method for blue-green algae in water body at present has Physical, chemical method and biological restoration, and Physical is turned with electric energy
Chemical energy is turned to, changes the molecular structure and property into water body or water body material, reaches killing, kill algae and decomposition, suction
Impurity in attached water body, reach the purpose of purification water system.Advantage is not destroy water body, noresidue, but physics killing is relation of equal quantity,
Killing life entity is bigger, and consumption is more, and killing is more, and energy consumptions are more, and water quality impurity is more, and power consumption is more.Comprise additionally in machine
Tool method manually salvages algae and takes the method dredged, and the former can only be used as easy supplementary means, at all can not be from root
Solve problem on this, and expend a large amount of manpower and materials, have little effect.Chemical method mainly uses various chemical algae removing agent, this
The chemical composition of a little algicide is the copper compound of ease of solubility, or chelated copper class material, to aquatic-organisms such as fish pasture and water
Produce a certain degree of injury and even result in death, and have carcinogenesis, also producing others, some are uncertain not
Good sequelae.Biological prosthetic algicide is the ten several active microorganisms and corresponding enzyme for processing eutrophication water, is
A kind of pure biological agent of All Pure Nature, the aquatile in water body and mankind etc. are not produced with any harm and side effect, produced
Product once put into water body, the microorganism prompt activation in product and the algae competition nutrient source in water, so that algae lacks battalion
Death is supported, is sunk under water, increasing microorganism continues the dead algae of degraded, until eliminating, water body is become clear.But biology
Preventing and treating of the method for method particularly restoration of the ecosystem for algal tufa in small range, FX is important method, but slowly effect, into
This height, the more difficult improvement for being generally applicable to large area, sudden algal tufa.Clay is deposited to water after simply blue-green algae is adsorbed except algae
Bottom, the algae for dropping to the bottom still live, and still can survive and amount reproduction over a period to come；Secondly, the bottom is dropped to
Algae is in anaerobic condition, if after rotting, can discharge hydrogen sulfide gas and Algae toxins, and Algae toxins can not decompose,
Can cause benthon after being spread in water body and spore biology is suffocated destructions, seriously causes bed mud anoxic, cause secondary
Pollution and biological death even release pernicious gas, further destroy aqueous bio chain.
The content of the invention
The technical problems to be solved by the invention：Removed for current method after blue-green algae simply adsorbs blue-green algae and be deposited to water
After bottom, dropping to the algae at the bottom can still be survived and amount reproduction over a period to come, and algae is rotted, cause benthon with
Spore biology is suffocated destruction and the drawbacks of secondary pollution of water, there is provided a kind of pass through adds five in algae pollution water body and aoxidized
Two vanadium carry out pre-oxidation treatment, then add calcium carbonate powder and hydrochloric acid, produce substantial amounts of CO2And heat, promote the cell of algae
Wall is opened, then adds calper calcium peroxide, produces the death that substantial amounts of oxygen promotes algae, and the calcium hydroxide of generation is used to adjust water body
PH value, algae is settled down in water, then by adding particle made from polyvinylamine, promotes algae to lose activity, be thoroughly dead,
It is eventually adding the processing method that bleaching powder carries out sterilizing to water body.Processing method of the present invention is quick, to algae removal rate
Height, to water body non-secondary pollution.
In order to solve the above technical problems, the present invention is using technical scheme as described below：
（1）Vanadic anhydride is taken to put into algae pollution water body, addition is 5~7mg/L, then starts agitator, if
It is 300~500r/min to put agitator speed, and stirring makes it be sufficiently mixed uniformly, 3~5h of pre-oxidation treatment, after pre-oxidizing,
Reduction rotating speed is 80r/min, stirs 10~20min；
（2）After above-mentioned stirring is complete, calcium carbonate is taken, is placed in grinding mill the 1~2h that mills, sieve to obtain 80~100 mesh
Calcium carbonate powder, calcium carbonate powder is uniformly sprinkled into algae pollution water body, the amount of being sprinkled into is 3~5mg/L, set agitator speed
For 300~400r/min, 3~4h of stirring reaction；
（3）After the completion for the treatment of its stirring reaction, by hydrochloric acid and algae pollution water body volume than 1:1000, by mass fraction be 30~
35% hydrochloric acid is put into algae pollution water body, 1~2h of stirring reaction under 160r/min, after question response, then by calper calcium peroxide and algae
Polluted-water mass ratio 2:3000, calper calcium peroxide is put into algae pollution water body, stirring makes it fully dissolve, and reacts 2~3h；
（4）After the completion of question response, polyvinylamine is taken, by it through gamma-ray irradiation, it is 5~7MeV to control irradiation energy, agent
Measure as 35~60kGy, be put into after irradiating 20~30min in container, by natural sodium bentonite, hydrogen peroxide and polyvinylamine quality
Than 1:2:1, the hydrogen peroxide that natural sodium bentonite and mass fraction are 17% is added in container and is well mixed, is with wavelength
350~370nm ultraviolet rays irradiates 40~50min；
（5）After the completion of to be irradiated, gained mixture is placed in 60~80 DEG C of vacuum tank and dries 1~2h, take out input
Milled in grinding mill, sieve 80~100 mesh particle, by 5~7mg/L of input amount, particle is put into algae pollution water body,
1~2h of stirring reaction under 160r/min, stand 2~3h；
（6）After the completion for the treatment of above-mentioned standing, by bleaching powder and algae pollution water body solid-to-liquid ratio 1:3000, it is dirty that bleaching powder is put into algae
Contaminate in water body, be uniformly mixed, sterilizing handles 2~3h, you can.
Compared with other method, advantageous effects are the present invention：
（1）Processing method of the present invention is quick, and more than 99.8% is up to algae removal rate；
（2）To water body non-secondary pollution after processing, suitable for large area, the improvement of sudden algal tufa.
Embodiment
Vanadic anhydride is taken to put into algae pollution water body first, addition is 5~7mg/L, then starts agitator, if
It is 300~500r/min to put agitator speed, and stirring makes it be sufficiently mixed uniformly, 3~5h of pre-oxidation treatment, after pre-oxidizing,
Reduction rotating speed is 80r/min, stirs 10~20min；Then after above-mentioned stirring is complete, calcium carbonate is taken, is placed in grinding mill
Mill 1~2h, sieve 80~100 mesh calcium carbonate powder, calcium carbonate powder is uniformly sprinkled into algae pollution water body, the amount of being sprinkled into
For 3~5mg/L, setting agitator speed is 300~400r/min, 3~4h of stirring reaction；After the completion for the treatment of its stirring reaction, press
Hydrochloric acid is with algae pollution water body volume than 1:1000, the hydrochloric acid that mass fraction is 30~35% is put into algae pollution water body,
1~2h of stirring reaction under 160r/min, after question response, then by calper calcium peroxide and algae pollution Water quality than 2:3000, by peroxide
Change in calcium input algae pollution water body, stirring makes it fully dissolve, and reacts 2~3h；After the completion of question response, polyvinylamine is taken, by it
Through gamma-ray irradiation, it is 5~7MeV to control irradiation energy, and dosage is 35~60kGy, is put into after irradiating 20~30min in container,
By natural sodium bentonite, hydrogen peroxide and polyvinylamine mass ratio 1:2:1, it is 17% by natural sodium bentonite and mass fraction
Hydrogen peroxide be added to container in be well mixed, with wavelength be 350~370nm ultraviolet rays irradiate 40~50min；It is to be irradiated
After the completion of, gained mixture is placed in 60~80 DEG C of vacuum tank and dries 1~2h, takes out in input grinding mill and mills, sieve
The particle of 80~100 mesh is obtained, by 5~7mg/L of input amount, particle is put into algae pollution water body, is stirred under 160r/min anti-
1~2h is answered, stands 2~3h；After the completion of finally treating above-mentioned standing, by bleaching powder and algae pollution water body solid-to-liquid ratio 1:3000, it will float
In white powder input algae pollution water body, it is uniformly mixed, sterilizing handles 2~3h, you can.
Example 1
Take vanadic anhydride to put into algae pollution water body first, addition 5mg/L, then start agitator, set
Agitator speed is 300r/min, and stirring makes it be sufficiently mixed uniformly, pre-oxidation treatment 3h, and after pre-oxidizing, reducing rotating speed is
80r/min, stir 10min；Then after above-mentioned stirring is complete, take calcium carbonate, be placed in grinding mill the 1h that mills, sieve 80
Purpose calcium carbonate powder, calcium carbonate powder is uniformly sprinkled into algae pollution water body, the amount of being sprinkled into is 3mg/L, sets agitator speed
For 300r/min, stirring reaction 3h；After the completion for the treatment of its stirring reaction, by hydrochloric acid and algae pollution water body volume than 1:1000, by matter
Measure the hydrochloric acid that fraction is 30% to put into algae pollution water body, the stirring reaction 1h under 160r/min, after question response, then by peroxidating
Calcium is with algae pollution Water quality than 2:3000, calper calcium peroxide is put into algae pollution water body, stirring makes it fully dissolve, and reacts
2h；After the completion of question response, polyvinylamine is taken, by it through gamma-ray irradiation, it is 5MeV to control irradiation energy, dosage 35kGy, spoke
According to being put into after 20min in container, by natural sodium bentonite, hydrogen peroxide and polyvinylamine mass ratio 1:2:1, natural sodium base is swollen
Profit soil and the hydrogen peroxide that mass fraction is 17% are added in container and are well mixed, and the ultraviolet rays for being 350nm with wavelength irradiates
40min；After the completion of to be irradiated, gained mixture is placed in 60 DEG C of vacuum tank and dries 1h, taken out in input grinding mill and mill,
Sieve 80 mesh particle, by input amount 5mg/L, particle is put into algae pollution water body, the stirring reaction 1h under 160r/min,
Stand 2h；After the completion of finally treating above-mentioned standing, by bleaching powder and algae pollution water body solid-to-liquid ratio 1:3000, it is dirty that bleaching powder is put into algae
Contaminate in water body, be uniformly mixed, sterilizing processing 2h, you can.Processing method of the present invention is quick, high to algae removal rate
Up to 99.85%；To water body non-secondary pollution after processing, suitable for large area, the improvement of sudden algal tufa.
Example 2
Take vanadic anhydride to put into algae pollution water body first, addition 6mg/L, then start agitator, set
Agitator speed is 400r/min, and stirring makes it be sufficiently mixed uniformly, pre-oxidation treatment 4h, and after pre-oxidizing, reducing rotating speed is
80r/min, stir 15min；Then after above-mentioned stirring is complete, calcium carbonate is taken, is placed in grinding mill the 1.5h that mills, is sieved
The calcium carbonate powder of 90 mesh, calcium carbonate powder is uniformly sprinkled into algae pollution water body, the amount of being sprinkled into is 4mg/L, sets agitator to turn
Speed is 350r/min, stirring reaction 3.5h；After the completion for the treatment of its stirring reaction, by hydrochloric acid and algae pollution water body volume than 1:1000,
The hydrochloric acid that mass fraction is 33% is put into algae pollution water body, the stirring reaction 1.5h under 160r/min, after question response, then pressed
Calper calcium peroxide is with algae pollution Water quality than 2:3000, calper calcium peroxide is put into algae pollution water body, stirring makes it fully dissolve,
React 2.5h；After the completion of question response, polyvinylamine is taken, by it through gamma-ray irradiation, it is 6MeV to control irradiation energy, and dosage is
47kGy, it is put into after irradiating 25min in container, by natural sodium bentonite, hydrogen peroxide and polyvinylamine mass ratio 1:2:1, by day
Right sodium bentonite and the hydrogen peroxide that mass fraction is 17% are added in container and are well mixed, and are that the ultraviolet of 360nm is penetrated with wavelength
Line irradiates 45min；After the completion of to be irradiated, gained mixture is placed in 70 DEG C of vacuum tank and dries 1.5h, taken out input and mill
Milled in machine, sieve 90 mesh particle, by input amount 6mg/L, particle is put into algae pollution water body, stirred under 160r/min
Reaction 1.5h is mixed, stands 2.5h；After the completion of finally treating above-mentioned standing, by bleaching powder and algae pollution water body solid-to-liquid ratio 1:3000, will
In bleaching powder input algae pollution water body, it is uniformly mixed, sterilizing processing 2.5h, you can.Processing method of the present invention takes effect
It hurry up, 99.91% be up to algae removal rate；After processing to water body non-secondary pollution, controlled suitable for large area, sudden algal tufa
Reason.
Example 3
Take vanadic anhydride to put into algae pollution water body first, addition 7mg/L, then start agitator, set
Agitator speed is 500r/min, and stirring makes it be sufficiently mixed uniformly, pre-oxidation treatment 5h, and after pre-oxidizing, reducing rotating speed is
80r/min, stir 20min；Then after above-mentioned stirring is complete, calcium carbonate is taken, is placed in grinding mill the 2h that mills, is sieved
The calcium carbonate powder of 100 mesh, calcium carbonate powder is uniformly sprinkled into algae pollution water body, the amount of being sprinkled into is 5mg/L, sets agitator to turn
Speed is 400r/min, stirring reaction 4h；After the completion for the treatment of its stirring reaction, by hydrochloric acid and algae pollution water body volume than 1:1000, will
The hydrochloric acid that mass fraction is 35% is put into algae pollution water body, the stirring reaction 2h under 160r/min, after question response, then by peroxide
Change calcium with algae pollution Water quality than 2:3000, calper calcium peroxide is put into algae pollution water body, stirring makes it fully dissolve, and reacts
3h；After the completion of question response, polyvinylamine is taken, by it through gamma-ray irradiation, it is 7MeV to control irradiation energy, dosage 60kGy, spoke
According to being put into after 30min in container, by natural sodium bentonite, hydrogen peroxide and polyvinylamine mass ratio 1:2:1, natural sodium base is swollen
Profit soil and the hydrogen peroxide that mass fraction is 17% are added in container and are well mixed, and the ultraviolet rays for being 370nm with wavelength irradiates
50min；After the completion of to be irradiated, gained mixture is placed in 80 DEG C of vacuum tank and dries 2h, taken out in input grinding mill and mill,
Sieve 100 mesh particle, by input amount 7mg/L, particle is put into algae pollution water body, the stirring reaction under 160r/min
2h, stand 3h；After the completion of finally treating above-mentioned standing, by bleaching powder and algae pollution water body solid-to-liquid ratio 1:3000, bleaching powder is put into
In algae pollution water body, it is uniformly mixed, sterilizing processing 3h, you can.Processing method of the present invention is quick, to algae removal
Rate is up to 99.96%；To water body non-secondary pollution after processing, suitable for large area, the improvement of sudden algal tufa.
Claims (1)
- A kind of 1. method for removing Measures of Algae in Water Body, it is characterised in that specifically minimizing technology is：（1）Vanadic anhydride is taken to put into algae pollution water body, addition is 5~7mg/L, then starts agitator, and setting is stirred It is 300~500r/min to mix device rotating speed, and stirring makes it be sufficiently mixed uniformly, 3~5h of pre-oxidation treatment, after pre-oxidizing, is reduced Rotating speed is 80r/min, stirs 10~20min；（2）After above-mentioned stirring is complete, take calcium carbonate, be placed in grinding mill the 1~2h that mills, sieve 80~100 mesh carbon Sour calcium powder, calcium carbonate powder is uniformly sprinkled into algae pollution water body, the amount of being sprinkled into is 3~5mg/L, and setting agitator speed is 300~400r/min, 3~4h of stirring reaction；（3）After the completion for the treatment of its stirring reaction, by hydrochloric acid and algae pollution water body volume than 1:1000, it is 30~35% by mass fraction Hydrochloric acid input algae pollution water body in, 1~2h of stirring reaction under 160r/min, after question response, then dirty by calper calcium peroxide and algae Water quality is contaminated than 2:3000, calper calcium peroxide is put into algae pollution water body, stirring makes it fully dissolve, and reacts 2~3h；（4）After the completion of question response, polyvinylamine is taken, by it through gamma-ray irradiation, it is 5~7MeV to control irradiation energy, and dosage is 35~60kGy, it is put into after irradiating 20~30min in container, by natural sodium bentonite, hydrogen peroxide and polyvinylamine mass ratio 1: 2:1, the hydrogen peroxide that natural sodium bentonite and mass fraction are 17% is added in container and is well mixed, with wavelength be 350~ 370nm ultraviolet rays irradiates 40~50min；（5）After the completion of to be irradiated, gained mixture is placed in 60~80 DEG C of vacuum tank and dries 1~2h, taken out input and mill Milled in machine, sieve 80~100 mesh particle, by 5~7mg/L of input amount, particle is put into algae pollution water body, 1~2h of stirring reaction under 160r/min, stand 2~3h；（6）After the completion for the treatment of above-mentioned standing, by bleaching powder and algae pollution water body solid-to-liquid ratio 1:3000, bleaching powder is put into algae pollution water In body, it is uniformly mixed, sterilizing handles 2~3h, you can.
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| CN109354143B (en) * | 2018-11-16 | 2022-02-18 | 同济大学 | Method for treating high algae content water based on calcium peroxide reinforced coagulation |
| CN110250202A (en) * | 2019-06-27 | 2019-09-20 | 苏州科技大学 | A kind of method of alga inhibitor and algal grown on control secondary settling tank pool wall |
| CN117069270B (en) * | 2023-08-18 | 2024-06-14 | 中国科学院地球化学研究所 | Method for increasing carbon sink of water body and relieving eutrophication of water body |
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| Publication number | Priority date | Publication date | Assignee | Title |
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|---|
| 絮凝剂强化微电解法处理罗丹明B废水的研究;段钧元等;《化工技术与开发》;20140228;第43卷(第2期);45-51 * |
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