CN105540798A - Compound denitrification agent for treating aquaculture wastewater and using method thereof - Google Patents
Compound denitrification agent for treating aquaculture wastewater and using method thereof Download PDFInfo
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- CN105540798A CN105540798A CN201610045577.3A CN201610045577A CN105540798A CN 105540798 A CN105540798 A CN 105540798A CN 201610045577 A CN201610045577 A CN 201610045577A CN 105540798 A CN105540798 A CN 105540798A
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- denitrification agent
- treatment
- breeding wastewater
- composite denitrification
- composite
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- 239000002351 wastewater Substances 0.000 title claims abstract description 51
- 238000000034 method Methods 0.000 title claims abstract description 18
- 150000001875 compounds Chemical class 0.000 title abstract 5
- 238000009360 aquaculture Methods 0.000 title abstract 4
- 244000144974 aquaculture Species 0.000 title abstract 4
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 39
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 18
- 239000000701 coagulant Substances 0.000 claims abstract description 16
- 159000000003 magnesium salts Chemical class 0.000 claims abstract description 16
- 229910019142 PO4 Inorganic materials 0.000 claims abstract description 5
- 239000010452 phosphate Substances 0.000 claims abstract description 5
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 claims abstract description 4
- 239000002131 composite material Substances 0.000 claims description 36
- 238000009395 breeding Methods 0.000 claims description 28
- 230000001488 breeding effect Effects 0.000 claims description 28
- 150000003016 phosphoric acids Chemical class 0.000 claims description 15
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 claims description 12
- TWRXJAOTZQYOKJ-UHFFFAOYSA-L Magnesium chloride Chemical compound [Mg+2].[Cl-].[Cl-] TWRXJAOTZQYOKJ-UHFFFAOYSA-L 0.000 claims description 10
- CSNNHWWHGAXBCP-UHFFFAOYSA-L Magnesium sulfate Chemical compound [Mg+2].[O-][S+2]([O-])([O-])[O-] CSNNHWWHGAXBCP-UHFFFAOYSA-L 0.000 claims description 8
- VSCWAEJMTAWNJL-UHFFFAOYSA-K aluminium trichloride Chemical compound Cl[Al](Cl)Cl VSCWAEJMTAWNJL-UHFFFAOYSA-K 0.000 claims description 8
- RUTXIHLAWFEWGM-UHFFFAOYSA-H iron(3+) sulfate Chemical compound [Fe+3].[Fe+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O RUTXIHLAWFEWGM-UHFFFAOYSA-H 0.000 claims description 7
- 229910000360 iron(III) sulfate Inorganic materials 0.000 claims description 7
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims description 6
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical group [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 6
- 229910001629 magnesium chloride Inorganic materials 0.000 claims description 5
- ZPWVASYFFYYZEW-UHFFFAOYSA-L dipotassium hydrogen phosphate Chemical compound [K+].[K+].OP([O-])([O-])=O ZPWVASYFFYYZEW-UHFFFAOYSA-L 0.000 claims description 4
- BNIILDVGGAEEIG-UHFFFAOYSA-L disodium hydrogen phosphate Chemical compound [Na+].[Na+].OP([O-])([O-])=O BNIILDVGGAEEIG-UHFFFAOYSA-L 0.000 claims description 4
- 229910000397 disodium phosphate Inorganic materials 0.000 claims description 4
- 235000019800 disodium phosphate Nutrition 0.000 claims description 4
- 229910052943 magnesium sulfate Inorganic materials 0.000 claims description 4
- 235000019341 magnesium sulphate Nutrition 0.000 claims description 4
- 229940045641 monobasic sodium phosphate Drugs 0.000 claims description 4
- VKJKEPKFPUWCAS-UHFFFAOYSA-M potassium chlorate Chemical compound [K+].[O-]Cl(=O)=O VKJKEPKFPUWCAS-UHFFFAOYSA-M 0.000 claims description 4
- AJPJDKMHJJGVTQ-UHFFFAOYSA-M sodium dihydrogen phosphate Chemical compound [Na+].OP(O)([O-])=O AJPJDKMHJJGVTQ-UHFFFAOYSA-M 0.000 claims description 4
- BZSXEZOLBIJVQK-UHFFFAOYSA-N 2-methylsulfonylbenzoic acid Chemical compound CS(=O)(=O)C1=CC=CC=C1C(O)=O BZSXEZOLBIJVQK-UHFFFAOYSA-N 0.000 claims description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 claims description 3
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 claims description 3
- 229910052742 iron Inorganic materials 0.000 claims description 3
- 239000001095 magnesium carbonate Substances 0.000 claims description 3
- ZLNQQNXFFQJAID-UHFFFAOYSA-L magnesium carbonate Chemical compound [Mg+2].[O-]C([O-])=O ZLNQQNXFFQJAID-UHFFFAOYSA-L 0.000 claims description 3
- 235000014380 magnesium carbonate Nutrition 0.000 claims description 3
- 229960001708 magnesium carbonate Drugs 0.000 claims description 3
- 229910000021 magnesium carbonate Inorganic materials 0.000 claims description 3
- 239000011591 potassium Substances 0.000 claims description 3
- 229910052700 potassium Inorganic materials 0.000 claims description 3
- SATVIFGJTRRDQU-UHFFFAOYSA-N potassium hypochlorite Chemical compound [K+].Cl[O-] SATVIFGJTRRDQU-UHFFFAOYSA-N 0.000 claims description 3
- SUKJFIGYRHOWBL-UHFFFAOYSA-N sodium hypochlorite Chemical compound [Na+].Cl[O-] SUKJFIGYRHOWBL-UHFFFAOYSA-N 0.000 claims description 3
- KCZFLPPCFOHPNI-UHFFFAOYSA-N alumane;iron Chemical compound [AlH3].[Fe] KCZFLPPCFOHPNI-UHFFFAOYSA-N 0.000 claims description 2
- 235000011147 magnesium chloride Nutrition 0.000 claims description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 abstract description 48
- 229910052757 nitrogen Inorganic materials 0.000 abstract description 24
- 230000008901 benefit Effects 0.000 abstract description 5
- 150000003839 salts Chemical class 0.000 abstract description 2
- 239000007800 oxidant agent Substances 0.000 abstract 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 7
- 238000006243 chemical reaction Methods 0.000 description 7
- 230000000694 effects Effects 0.000 description 5
- 238000005259 measurement Methods 0.000 description 5
- 244000144972 livestock Species 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- QGZKDVFQNNGYKY-UHFFFAOYSA-N ammonia Natural products N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 3
- 239000003814 drug Substances 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 2
- 229910021529 ammonia Inorganic materials 0.000 description 2
- 230000031018 biological processes and functions Effects 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 description 2
- 229910052698 phosphorus Inorganic materials 0.000 description 2
- 239000011574 phosphorus Substances 0.000 description 2
- 244000144977 poultry Species 0.000 description 2
- 238000002360 preparation method Methods 0.000 description 2
- 238000002203 pretreatment Methods 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 230000035484 reaction time Effects 0.000 description 2
- 206010059410 Faecaluria Diseases 0.000 description 1
- JLVVSXFLKOJNIY-UHFFFAOYSA-N Magnesium ion Chemical compound [Mg+2] JLVVSXFLKOJNIY-UHFFFAOYSA-N 0.000 description 1
- JVMRPSJZNHXORP-UHFFFAOYSA-N ON=O.ON=O.ON=O.N Chemical compound ON=O.ON=O.ON=O.N JVMRPSJZNHXORP-UHFFFAOYSA-N 0.000 description 1
- MXZRMHIULZDAKC-UHFFFAOYSA-L ammonium magnesium phosphate Chemical compound [NH4+].[Mg+2].[O-]P([O-])([O-])=O MXZRMHIULZDAKC-UHFFFAOYSA-L 0.000 description 1
- 244000052616 bacterial pathogen Species 0.000 description 1
- 230000003851 biochemical process Effects 0.000 description 1
- 238000009388 chemical precipitation Methods 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 230000001112 coagulating effect Effects 0.000 description 1
- 230000006378 damage Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- DNJIEGIFACGWOD-UHFFFAOYSA-N ethanethiol Chemical compound CCS DNJIEGIFACGWOD-UHFFFAOYSA-N 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 229910001425 magnesium ion Inorganic materials 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 229910052567 struvite Inorganic materials 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
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—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
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/20—Nature of the water, waste water, sewage or sludge to be treated from animal husbandry
Landscapes
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Inorganic Chemistry (AREA)
- Removal Of Specific Substances (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
The invention relates to a compound denitrification agent for treating aquaculture wastewater and a using method thereof. The compound denitrification agent is prepared from, by weight, 10%-25% of an oxidizing agent, 20%-40% of magnesium salt, 7%-20% of phosphate, 1%-5% of a coagulant aid or ferric salt and the balance water. The using method comprises the steps that the compounded compound denitrification agent is put into the aquaculture wastewater to be treated according to the volume ratio of 0.1%-2%, reacting is performed for 20-150 minutes, and then the nitrogen content of the aquaculture wastewater can reach the standard. The compound denitrification agent has the advantages of being convenient to use and capable of reaching the standard through one-time removing.
Description
Technical field
The present invention relates to environmental pollution water-treatment technology field, particularly a kind of Composite denitrification agent for the treatment of breeding wastewater and using method thereof.
Background technology
Along with the development of China's livestock industry, inter-industry competition is growing more intense, and mass-producing, the intensivization development of livestock industry have become a kind of inexorable trend, and unified management is conducive to reducing costs and increasing economic efficiency; Pig industry is as the major portion of livestock and poultry breeding industry, its rinse pig house cleaning water, rush the breeding wastewater that liquid dung and fecaluria form, because its quantity discharged is large, pollution load is high, produce stench containing a large amount of organism, nitrogen, phosphorus, suspended substance and pathogenic bacterium, become the Focal point and difficult point in current livestock and poultry breeding industry prevention and cure of pollution; And its fund input in sewage disposal is limited because pig farm economic benefit is not high, need to seek a kind of less investment, the treatment process that treatment effect is good.
The breeding wastewater being rich in ammonia nitrogen in high density generally adopts the method such as biological process, chemical precipitation (MAP) method to process; Biochemical process because treatment capacity is large, low cost and other advantages and being used widely, breeding wastewater is after biochemical treatment, although COD, ammonia nitrogen, total phosphorus can reach emission standard substantially, and total nitrogen easily exceeds standard.
Total nitrogen comprises organonitrogen and inorganic nitrogen, and inorganic nitrogen is made up of ammonia nitrogen, nitric nitrogen and nitrite nitrogen; After biochemical treatment, waste water total nitrogen is not up to standard, mainly because organonitrogen cannot effectively be degraded in biological process.MAP method is by adding phosphoric acid salt and magnesium salts in waste water, and the ammonia nitrogen in solution is combined and generates magnesium ammonium phosphate sediment, thus realizes the object removing ammonia nitrogen.But because precipitation dosing is large, and ammonia nitrogen cannot once be removed up to standard, thus limits promoting the use of of MAP method.Adopt single coagulating agent often to can not get desirable treatment effect, therefore, the composite operation technique of medicament becomes the study hotspot of current water treatment field.
Summary of the invention
The object of the invention is to overcome deficiency of the prior art, a kind of Composite denitrification agent for the treatment of breeding wastewater and using method thereof are provided, the raw material sources of this Composite denitrification agent are extensive, preparation method is simple, have simultaneously easy to use, once remove advantage up to standard.
Technical scheme provided by the invention is:
For the treatment of a Composite denitrification agent for breeding wastewater, composed of the following components by weight percentage: 10% ~ 25% oxygenant, 20% ~ 40% magnesium salts, 7% ~ 20% phosphoric acid salt, 1% ~ 5% coagulant aids or molysite, all the other are water.
Preferably, described oxygenant is one or more in Potcrate, sodium chlorate, clorox, potassium hypochlorite or hydrogen peroxide.
Preferably, described magnesium salts is one or more mixing in magnesium chloride, magnesium sulfate or magnesiumcarbonate.
Preferably, described phosphoric acid salt is one or more in potassium primary phosphate, dipotassium hydrogen phosphate, SODIUM PHOSPHATE, MONOBASIC or Sodium phosphate dibasic.
Preferably, described coagulant aids is polymerize aluminum chloride, bodied ferric sulfate or aluminium iron polychloride; Described molysite is iron(ic) chloride or ferric sulfate; Above-mentioned coagulant aids and molysite can be used alone, also can be used in combination according to a certain percentage.
The using method of above-mentioned a kind of Composite denitrification agent for the treatment of breeding wastewater is as follows:
Put in pending breeding wastewater by composite good Composite denitrification agent, dosage is the volume ratio of 0.1% ~ 2%, and the reaction times is 20 ~ 150 minutes; Reaction terminates to make the nitrogen content in waste water up to standard, reaches the effect that disposable removal is up to standard.
The dosage of above-mentioned Composite denitrification agent is determined according to the nitrogen content of pending breeding wastewater; If the nitrogen content in waste water is high, and follow-up treatment process has requirement, only need carry out pre-treatment to waste water reduces certain nitrogen content, then also can reduce dosage in proportion to reach pretreating effect.
One provided by the present invention, for the treatment of the agent of breeding wastewater Composite denitrification and using method thereof, compared with prior art, has the following advantages:
Composite denitrification agent of the present invention contains oxygenant and coagulant aids, when this Composite denitrification agent is put in breeding wastewater by a certain percentage, the oxygenant comprised can carry out oxide treatment to the nitrogenous substances in waste water, C-N key in effective destruction organonitrogen, makes it be converted into ammonium nitrogen or nitric nitrogen; Simultaneously coagulant aids can carry out coagulating treatment to nitrogenous substances, and with phosphate radical in solution, magnesium ion generates double salt and sedimentation is removed.
Composite denitrification agent of the present invention both can as the pre-treatment of high-concentration ammonia nitrogenous wastewater, also can as the advanced treatment of Low Concentration Ammonia Containing Wastewater.Realize medicament once to add, reduce labor management and running cost.
Composite denitrification agent raw materials wide material sources of the present invention, preparation method is simple, can on-the-spotly directly prepare, and also can produce by large-scale industrial.
Embodiment
Below in conjunction with embodiment, the present invention is further illustrated:
Embodiment 1
Component for the treatment of the Composite denitrification agent of breeding wastewater is: 25% oxygenant, 20% magnesium salts, 7% phosphoric acid salt, 1% molysite, and all the other are water.Oxygenant is Potcrate, and magnesium salts is magnesiumcarbonate, and phosphoric acid salt is potassium primary phosphate, and molysite is ferric sulfate.
Get the water outlet on certain pig farm, add the Composite denitrification agent of 1% volume ratio, react 150 minutes, after reaction terminates, total nitrogen content in wastewater measurement.Determination of Total Nitrogen in Waste Water concentration is down to 12.83mg/L by initial 1210mg/L, reaches emission standard.
Embodiment 2
Component for the treatment of the Composite denitrification agent of breeding wastewater is: 10% oxygenant, 40% magnesium salts, 20% phosphoric acid salt, 5% coagulant aids, and all the other are water.Oxygenant is clorox, and magnesium salts is magnesium sulfate, and phosphoric acid salt is Sodium phosphate dibasic, and coagulant aids is bodied ferric sulfate.
Get the water outlet on certain pig farm, add the Composite denitrification agent of 2% volume ratio, react 60 minutes, after reaction terminates, total nitrogen content in wastewater measurement.Determination of Total Nitrogen in Waste Water concentration is down to 14.39mg/L by initial 1290mg/L, reaches emission standard.
Embodiment 3
Component for the treatment of the Composite denitrification agent of breeding wastewater is: 20% oxygenant, 40% magnesium salts, 20% phosphoric acid salt, 5% coagulant aids, and all the other are water.Oxygenant is hydrogen peroxide, and magnesium salts is magnesium chloride, and phosphoric acid salt is the mixture of dipotassium hydrogen phosphate and Sodium phosphate dibasic 1:1 mixing in mass ratio, and coagulant aids is polymerize aluminum chloride.
Get the water outlet on certain pig farm, add the Composite denitrification agent of 1 ‰ volume ratios, react 40 minutes, after reaction terminates, total nitrogen content in wastewater measurement.Determination of Total Nitrogen in Waste Water concentration is down to 7.42mg/L by initial 940mg/L, reaches emission standard.
Embodiment 4
Component for the treatment of the Composite denitrification agent of breeding wastewater is: 15% oxygenant, 30% magnesium salts, 15% phosphoric acid salt, 3% coagulant aids and molysite mixture, and all the other are water.Oxygenant is potassium hypochlorite, and magnesium salts is magnesium chloride, and phosphoric acid salt is SODIUM PHOSPHATE, MONOBASIC, and coagulant aids and molysite mixture are the composition of PAFS and ferric sulfate 1:1 mixing in mass ratio.
Get the water outlet on certain pig farm, add the Composite denitrification agent of 1 ‰ volume ratios, react 20 minutes, after reaction terminates, total nitrogen content in wastewater measurement.Determination of Total Nitrogen in Waste Water concentration is down to 4.58mg/L by initial 67mg/L, reaches emission standard.
Embodiment 5:
Component for the treatment of the Composite denitrification agent of breeding wastewater is: 25% oxygenant, 35% magnesium salts, 15% phosphoric acid salt, 2% molysite, and all the other are water.Oxygenant is sodium chlorate, and magnesium salts is magnesium sulfate, and phosphoric acid salt is SODIUM PHOSPHATE, MONOBASIC, and molysite is iron(ic) chloride.
Get the water outlet on certain pig farm, add the Composite denitrification agent of 0.1 ‰ volume ratios, react 40 minutes, after reaction terminates, total nitrogen content in wastewater measurement.Determination of Total Nitrogen in Waste Water concentration is down to 12.61mg/L by initial 24mg/L, reaches emission standard.
Embodiment 6: contrast experiment
Experimental group (the present invention): get 20% Potcrate, 40% magnesium chloride, 20% dipotassium hydrogen phosphate, 5% polymerize aluminum chloride, all the other are water.
Control group: certain commercially available NH_3-N treating agent.
Two kinds of denitrogenation processing agent are applied to certain pig farm water outlet, method is identical and as follows: in this Pig raising wastewater, add above-mentioned two kinds of medicaments, add-on is 1% of wastewater volume, react 30 minutes, reaction terminates rear mensuration residue total nitrogen content, its result is experimental group: 12.6mg/L, control group: 48.5mg/L.As can be seen here, under the prerequisite that, the reaction times identical at dosage is identical, the present invention is better to Pig raising wastewater denitrification effect.
Claims (8)
1. the Composite denitrification agent for the treatment of breeding wastewater, it is characterized in that: described Composite denitrification agent is composed of the following components by weight percentage: 10% ~ 25% oxygenant, 20% ~ 40% magnesium salts, 7% ~ 20% phosphoric acid salt, 1% ~ 5% coagulant aids or molysite, all the other are water.
2. a kind of Composite denitrification agent for the treatment of breeding wastewater according to claim 1, is characterized in that: described oxygenant is one or more in Potcrate, sodium chlorate, clorox, potassium hypochlorite or hydrogen peroxide.
3. a kind of Composite denitrification agent for the treatment of breeding wastewater according to claim 1, is characterized in that: described magnesium salts is one or more mixing in magnesium chloride, magnesium sulfate or magnesiumcarbonate.
4. a kind of Composite denitrification agent for the treatment of breeding wastewater according to claim 1, is characterized in that: described phosphoric acid salt is one or more in potassium primary phosphate, dipotassium hydrogen phosphate, SODIUM PHOSPHATE, MONOBASIC or Sodium phosphate dibasic.
5. a kind of Composite denitrification agent for the treatment of breeding wastewater according to claim 1, is characterized in that: described coagulant aids is one or more of polymerize aluminum chloride, bodied ferric sulfate or aluminium iron polychloride.
6. a kind of Composite denitrification agent for the treatment of breeding wastewater according to claim 1, is characterized in that: described molysite is iron(ic) chloride or ferric sulfate.
7. a kind of Composite denitrification agent for the treatment of breeding wastewater according to claim 1, is characterized in that: described coagulant aids and described molysite are mixed in proportion use.
8. the using method of a kind of Composite denitrification agent for the treatment of breeding wastewater according to claim 1-7, it is characterized in that: by composite good described Composite denitrification agent by 0.1% ~ 2% dosage put in pending breeding wastewater, react 20 ~ 150 minutes.
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106186105A (en) * | 2016-08-24 | 2016-12-07 | 米桂琼 | A kind of preparation method of alkaline sewage inorganic agent |
CN106186226A (en) * | 2016-08-25 | 2016-12-07 | 桂林浩新科技服务有限公司 | A kind of water quality cleansing agent and preparation method thereof |
CN106957070A (en) * | 2017-03-20 | 2017-07-18 | 浙江清环保工程有限公司 | A kind of rapidly and efficiently ammonia nitrogen removal agent and its preparation method and application |
CN107473396A (en) * | 2017-07-26 | 2017-12-15 | 明光市永言水产食品有限公司 | A kind of water body organic improving preparation |
Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS53667A (en) * | 1976-06-22 | 1978-01-06 | Kubota Ltd | Process for removing nitrous acid netrogen |
KR20050079380A (en) * | 2004-02-05 | 2005-08-10 | 김두섭 | Method for removal of noxious nitrogen in industrial waste water |
CN1837082A (en) * | 2006-04-05 | 2006-09-27 | 深圳市金达莱环保有限公司 | Treatment process for removing ammonia nitrogen in waste water |
WO2008017137A1 (en) * | 2006-08-11 | 2008-02-14 | The University Of British Columbia | Method and apparatus using hydrogen peroxide and microwave system for slurries treatment |
CN101555077A (en) * | 2008-04-11 | 2009-10-14 | 中国科学院广州地球化学研究所 | Method for treating highly concentrated ammonian wastewater with poor biodegradability by using a multiple-technique combination |
CN101987766A (en) * | 2010-11-08 | 2011-03-23 | 华南理工大学 | Standard treatment method for concentrated leachate |
CN102070263A (en) * | 2010-11-25 | 2011-05-25 | 杭州诚洁环保有限公司 | Coking phenol cyanogen sewage treating method |
CN102153180A (en) * | 2011-05-27 | 2011-08-17 | 四川美立方环保科技有限公司 | Multiple heavy metal synchronous coprecipitation coagulation composition agent and method for treating heavy metal wastewater |
CN102765829A (en) * | 2011-05-04 | 2012-11-07 | 上海焦化有限公司 | Treatment method for urea-containing high concentration copper ammonium wastewater |
-
2016
- 2016-01-22 CN CN201610045577.3A patent/CN105540798A/en active Pending
Patent Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS53667A (en) * | 1976-06-22 | 1978-01-06 | Kubota Ltd | Process for removing nitrous acid netrogen |
KR20050079380A (en) * | 2004-02-05 | 2005-08-10 | 김두섭 | Method for removal of noxious nitrogen in industrial waste water |
CN1837082A (en) * | 2006-04-05 | 2006-09-27 | 深圳市金达莱环保有限公司 | Treatment process for removing ammonia nitrogen in waste water |
WO2008017137A1 (en) * | 2006-08-11 | 2008-02-14 | The University Of British Columbia | Method and apparatus using hydrogen peroxide and microwave system for slurries treatment |
CN101555077A (en) * | 2008-04-11 | 2009-10-14 | 中国科学院广州地球化学研究所 | Method for treating highly concentrated ammonian wastewater with poor biodegradability by using a multiple-technique combination |
CN101987766A (en) * | 2010-11-08 | 2011-03-23 | 华南理工大学 | Standard treatment method for concentrated leachate |
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