CN110606574A - Ammonia nitrogen eliminating bacteriostat - Google Patents

Ammonia nitrogen eliminating bacteriostat Download PDF

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Publication number
CN110606574A
CN110606574A CN201910925555.XA CN201910925555A CN110606574A CN 110606574 A CN110606574 A CN 110606574A CN 201910925555 A CN201910925555 A CN 201910925555A CN 110606574 A CN110606574 A CN 110606574A
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CN
China
Prior art keywords
ammonia nitrogen
parts
bacteriostat
eliminating
nitrogen eliminating
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Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201910925555.XA
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Chinese (zh)
Inventor
谢长明
刘贵庆
邓永洪
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Taisheng Environmental Protection Equipment (ma'anshan) Co Ltd
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Taisheng Environmental Protection Equipment (ma'anshan) Co Ltd
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Priority to CN201910925555.XA priority Critical patent/CN110606574A/en
Publication of CN110606574A publication Critical patent/CN110606574A/en
Pending legal-status Critical Current

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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/02Biological treatment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • C02F3/347Use of yeasts or fungi
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/20Nature of the water, waste water, sewage or sludge to be treated from animal husbandry
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/02Odour removal or prevention of malodour
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

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  • Life Sciences & Earth Sciences (AREA)
  • Water Supply & Treatment (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Microbiology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Mycology (AREA)
  • Molecular Biology (AREA)
  • Agricultural Chemicals And Associated Chemicals (AREA)

Abstract

The invention discloses an ammonia nitrogen eliminating bacteriostat, which is characterized by comprising the following components in part by weight: 20-40 parts of yeast, 20-40 parts of lactic acid bacteria, 20-40 parts of photosynthetic bacteria, 1-5 parts of nano titanium dioxide, 10-50 parts of rice washing water and 1-5 parts of surfactant. The ammonia nitrogen eliminating bacteriostat comprises the following steps: mixing the ammonia nitrogen eliminating bacteriostat and the livestock and poultry excrement. The invention has the characteristics of affinity to human bodies, cultured animals and environment, safety and environmental protection.

Description

Ammonia nitrogen eliminating bacteriostat
Technical Field
The invention belongs to the field of pollution treatment, and particularly relates to an ammonia nitrogen eliminating bacteriostatic agent.
Background
Ammonia nitrogen refers to nitrogen present in the water as free ammonia and ammonium ions. The nitrogen content of the animal organic matter is generally higher than that of the plant organic matter. Meanwhile, nitrogen-containing organic matters in human and animal excreta are unstable and are easily decomposed into ammonia. Thus, an increase in the level of ammonia nitrogen in water refers to the presence of bound nitrogen in the form of ammonia or ammonium ions.
The ammonia nitrogen in the water can be converted into nitrite under certain conditions, and if the water is drunk for a long time, the nitrite in the water is combined with protein to form nitrosamine, which is a strong carcinogen and extremely unfavorable for the human health.
The main harm effect of ammonia nitrogen on aquatic organisms is free ammonia, the toxicity of the free ammonia is dozens of times higher than that of ammonium salt, and the free ammonia increases with the increase of alkalinity. The toxicity of ammonia nitrogen has a close relationship with the pH value and the water temperature of the pond water, and under the general condition, the higher the pH value and the water temperature is, the stronger the toxicity is, and the harm to fish is similar to that of nitrite.
The harm of ammonia nitrogen to aquatic life is divided into acute and chronic. The harm of chronic ammonia nitrogen poisoning is as follows: decreased feeding, slower growth, tissue damage, and reduced oxygen transport between tissues. The fish is sensitive to ammonia nitrogen in water, and when the ammonia nitrogen content is high, the fish can die. The acute ammonia nitrogen poisoning hazard is as follows: the water organisms appear to be excited, lose balance in water, twitch, and even die in severe cases.
Therefore, the search for an ammonia nitrogen eliminating bacteriostatic agent with simple formula is urgent.
Disclosure of Invention
The invention aims to provide an ammonia nitrogen eliminating bacteriostatic agent, which comprises the following components:
20-40 parts of yeast, 20-40 parts of lactic acid bacteria, 20-40 parts of photosynthetic bacteria, 1-5 parts of nano titanium dioxide, 10-50 parts of rice washing water and 1-5 parts of surfactant.
As a preferred scheme, the ammonia nitrogen eliminating bacteriostatic agent comprises:
25-40 parts of yeast, 20-25 parts of lactic acid bacteria, 25-35 parts of photosynthetic bacteria, 2-4 parts of nano titanium dioxide, 15-45 parts of rice washing water and 2-4 parts of surfactant.
As a preferred scheme, the ammonia nitrogen eliminating bacteriostat consists of the following components:
25-40 parts of yeast, 20-25 parts of lactic acid bacteria, 25-35 parts of photosynthetic bacteria, 2-4 parts of nano titanium dioxide, 15-45 parts of rice washing water and 2-4 parts of surfactant.
Preferably, the weight ratio of the yeast to the lactic acid bacteria is 1.2-1.5: 1.
Preferably, the surfactant is at least one selected from sodium lauryl sulfate, sodium cetyl sulfate and sodium stearyl sulfate.
More preferably, the surfactant is a mixture of sodium cetyl sulfate and sodium stearyl sulfate in a weight ratio of 1.5-2: 1.
In the invention, the preparation method of the ammonia nitrogen eliminating bacteriostatic agent comprises the following steps: the components are mixed evenly.
As a preferred scheme, the application steps of the ammonia nitrogen eliminating bacteriostat comprise: mixing the ammonia nitrogen eliminating bacteriostat and the livestock and poultry excrement.
Preferably, the application environment is as follows: and (4) places with sufficient light sources.
Preferably, when the environment is indoor, the mixture of the ammonia nitrogen eliminating bacteriostat and the livestock and poultry excrement is irradiated by full illumination of an incandescent lamp.
The invention has the characteristics of affinity to human bodies, cultured animals and environment, safety and environmental protection.
The product of the invention has the following action principle and characteristics: the product has the characteristics that the product must be used in places with sufficient light sources, the ammonia nitrogen in the air and in the product is eliminated mainly by utilizing the catalytic action of sunlight, and the effect is produced by full illumination of incandescent lamps in indoor use; the lactobacillus is used as a basic raw material for digestion to generate the fermentation effect of the odor source, the spraying amount and the spraying period can be adjusted according to the weight of the odor, and the fly can be reduced after the use, thereby reducing the fly oviposition and being the best natural product for producing the organic fertilizer.
Additional features and advantages of the invention will be set forth in the detailed description which follows.
Detailed Description
Preferred embodiments of the present invention will be described in more detail below. While the following describes preferred embodiments of the present invention, it should be understood that the present invention may be embodied in various forms and should not be limited by the embodiments set forth herein. Rather, these embodiments are provided so that this disclosure will be thorough and complete, and will fully convey the scope of the invention to those skilled in the art.
In the embodiment, a Naeseler colorimetric method is adopted for detecting ammonia nitrogen.
Example 1
The embodiment provides an ammonia nitrogen eliminating bacteriostatic agent, which comprises the following components:
32.5 parts of microzyme, 22.5 parts of lactic acid bacteria, 30 parts of photosynthetic bacteria, 3 parts of nano titanium dioxide, 30 parts of rice washing water and 3 parts of surfactant.
The surfactant is a mixture of sodium hexadecyl sulfate and sodium octadecyl sulfate, and the weight ratio of the sodium hexadecyl sulfate to the sodium octadecyl sulfate is 1.75: 1.
The preparation method of the ammonia nitrogen eliminating bacteriostatic agent comprises the following steps: the components are mixed evenly.
Mixing the obtained ammonia nitrogen eliminating bacteriostat with a certain livestock and poultry excrement sample s1 in a place with sufficient light source, measuring the ammonia nitrogen content at irregular intervals, stopping treatment if the ammonia nitrogen content is less than 5 percent of the original ammonia nitrogen content, and adding the certain prepared ammonia nitrogen eliminating bacteriostat if the ammonia nitrogen content is not satisfied until the ammonia nitrogen content is less than 5 percent of the original ammonia nitrogen content.
Example 2
The embodiment provides an ammonia nitrogen eliminating bacteriostatic agent, which comprises the following components:
27 parts of saccharomycete, 22.5 parts of lactic acid bacteria, 30 parts of photosynthetic bacteria, 3 parts of nano titanium dioxide, 30 parts of rice washing water and 3 parts of surfactant.
The surfactant is a mixture of sodium hexadecyl sulfate and sodium octadecyl sulfate, and the weight ratio of the sodium hexadecyl sulfate to the sodium octadecyl sulfate is 1.75: 1.
The preparation method of the ammonia nitrogen eliminating bacteriostatic agent comprises the following steps: the components are mixed evenly.
Mixing the obtained ammonia nitrogen eliminating bacteriostat with a certain livestock and poultry excrement sample s1 in a place with sufficient light source, measuring the ammonia nitrogen content at irregular intervals, stopping treatment if the ammonia nitrogen content is less than 5 percent of the original ammonia nitrogen content, and adding the certain prepared ammonia nitrogen eliminating bacteriostat if the ammonia nitrogen content is not satisfied until the ammonia nitrogen content is less than 5 percent of the original ammonia nitrogen content.
Example 3
The embodiment provides an ammonia nitrogen eliminating bacteriostatic agent, which comprises the following components:
40 parts of saccharomycetes, 26.7 parts of lactic acid bacteria, 30 parts of photosynthetic bacteria, 3 parts of nano titanium dioxide, 30 parts of rice washing water and 3 parts of surfactant.
The surfactant is a mixture of sodium hexadecyl sulfate and sodium octadecyl sulfate, and the weight ratio of the sodium hexadecyl sulfate to the sodium octadecyl sulfate is 1.75: 1.
The preparation method of the ammonia nitrogen eliminating bacteriostatic agent comprises the following steps: the components are mixed evenly.
Mixing the obtained ammonia nitrogen eliminating bacteriostat with a certain livestock and poultry excrement sample s1 in a place with sufficient light source, measuring the ammonia nitrogen content at irregular intervals, stopping treatment if the ammonia nitrogen content is less than 5 percent of the original ammonia nitrogen content, and adding the certain prepared ammonia nitrogen eliminating bacteriostat if the ammonia nitrogen content is not satisfied until the ammonia nitrogen content is less than 5 percent of the original ammonia nitrogen content.
Example 4
The embodiment provides an ammonia nitrogen eliminating bacteriostatic agent, which comprises the following components:
20 parts of microzyme, 20 parts of lactic acid bacteria, 30 parts of photosynthetic bacteria, 3 parts of nano titanium dioxide, 30 parts of rice washing water and 3 parts of surfactant.
The surfactant is a mixture of sodium hexadecyl sulfate and sodium octadecyl sulfate, and the weight ratio of the sodium hexadecyl sulfate to the sodium octadecyl sulfate is 1.75: 1.
The preparation method of the ammonia nitrogen eliminating bacteriostatic agent comprises the following steps: the components are mixed evenly.
Mixing the obtained ammonia nitrogen eliminating bacteriostat with a certain livestock and poultry excrement sample s1 in a place with sufficient light source, measuring the ammonia nitrogen content at irregular intervals, stopping treatment if the ammonia nitrogen content is less than 5 percent of the original ammonia nitrogen content, and adding the certain prepared ammonia nitrogen eliminating bacteriostat if the ammonia nitrogen content is not satisfied until the ammonia nitrogen content is less than 5 percent of the original ammonia nitrogen content.
Example 5
The embodiment provides an ammonia nitrogen eliminating bacteriostatic agent, which comprises the following components:
20 parts of microzyme, 20 parts of lactic acid bacteria, 40 parts of photosynthetic bacteria, 3 parts of nano titanium dioxide, 30 parts of rice washing water and 3 parts of surfactant.
The surfactant is a mixture of sodium hexadecyl sulfate and sodium octadecyl sulfate, and the weight ratio of the sodium hexadecyl sulfate to the sodium octadecyl sulfate is 1.75: 1.
The preparation method of the ammonia nitrogen eliminating bacteriostatic agent comprises the following steps: the components are mixed evenly.
Mixing the obtained ammonia nitrogen eliminating bacteriostat with a certain livestock and poultry excrement sample s1 in a place with sufficient light source, measuring the ammonia nitrogen content at irregular intervals, stopping treatment if the ammonia nitrogen content is less than 5 percent of the original ammonia nitrogen content, and adding the certain prepared ammonia nitrogen eliminating bacteriostat if the ammonia nitrogen content is not satisfied until the ammonia nitrogen content is less than 5 percent of the original ammonia nitrogen content.
Example 6
The embodiment provides an ammonia nitrogen eliminating bacteriostatic agent, which comprises the following components:
20 parts of microzyme, 20 parts of lactic acid bacteria, 20 parts of photosynthetic bacteria, 3 parts of nano titanium dioxide, 30 parts of rice washing water and 3 parts of surfactant.
The surfactant is a mixture of sodium hexadecyl sulfate and sodium octadecyl sulfate, and the weight ratio of the sodium hexadecyl sulfate to the sodium octadecyl sulfate is 1.75: 1.
The preparation method of the ammonia nitrogen eliminating bacteriostatic agent comprises the following steps: the components are mixed evenly.
Mixing the obtained ammonia nitrogen eliminating bacteriostat with a certain livestock and poultry excrement sample s1 in a place with sufficient light source, measuring the ammonia nitrogen content at irregular intervals, stopping treatment if the ammonia nitrogen content is less than 5 percent of the original ammonia nitrogen content, and adding the certain prepared ammonia nitrogen eliminating bacteriostat if the ammonia nitrogen content is not satisfied until the ammonia nitrogen content is less than 5 percent of the original ammonia nitrogen content.
By comparing the examples, the difference of the usage amount of the ammonia nitrogen eliminating bacteriostat in the examples 1-3 is smaller, and the usage amount of the ammonia nitrogen eliminating bacteriostat in the examples 4-6 is about 1.2-1.5 times of that of the ammonia nitrogen eliminating bacteriostat in the examples 1-3, compared with the livestock and poultry excrement sample with the same quality.
Having described embodiments of the present invention, the foregoing description is intended to be exemplary, not exhaustive, and not limited to the embodiments disclosed. Many modifications and variations will be apparent to those of ordinary skill in the art without departing from the scope and spirit of the described embodiments.

Claims (10)

1. The utility model provides an ammonia nitrogen elimination bacteriostat which characterized in that, this ammonia nitrogen elimination bacteriostat includes:
20-40 parts of yeast, 20-40 parts of lactic acid bacteria, 20-40 parts of photosynthetic bacteria, 1-5 parts of nano titanium dioxide, 10-50 parts of rice washing water and 1-5 parts of surfactant.
2. The ammonia nitrogen eliminating bacteriostatic agent of claim 1, wherein the ammonia nitrogen eliminating bacteriostatic agent comprises:
25-40 parts of yeast, 20-25 parts of lactic acid bacteria, 25-35 parts of photosynthetic bacteria, 2-4 parts of nano titanium dioxide, 15-45 parts of rice washing water and 2-4 parts of surfactant.
3. The ammonia nitrogen eliminating bacteriostat of claim 2, wherein the ammonia nitrogen eliminating bacteriostat consists of the following components:
25-40 parts of yeast, 20-25 parts of lactic acid bacteria, 25-35 parts of photosynthetic bacteria, 2-4 parts of nano titanium dioxide, 15-45 parts of rice washing water and 2-4 parts of surfactant.
4. The ammonia nitrogen eliminating bacteriostat according to claim 1, wherein the weight ratio of the yeast and the lactic acid bacteria is 1.2-1.5: 1.
5. The ammonia nitrogen eliminating bacteriostat of claim 1, wherein the surfactant is selected from at least one of sodium dodecyl sulfate, sodium hexadecyl sulfate and sodium octadecyl sulfate.
6. The ammonia nitrogen eliminating bacteriostat of claim 1, wherein the surfactant is a mixture of sodium hexadecyl sulfate and sodium octadecyl sulfate in a weight ratio of 1.5-2: 1.
7. The ammonia nitrogen eliminating bacteriostat of claim 1, wherein the preparation method of the ammonia nitrogen eliminating bacteriostat comprises the following steps: the components are mixed evenly.
8. The ammonia nitrogen eliminating bacteriostatic agent of claim 1, wherein the step of applying the ammonia nitrogen eliminating bacteriostatic agent comprises: mixing the ammonia nitrogen eliminating bacteriostat and the livestock and poultry excrement.
9. The ammonia nitrogen eliminating bacteriostatic agent according to claim 8, wherein the applied environment is as follows: and (4) places with sufficient light sources.
10. The ammonia nitrogen eliminating bacteriostat according to claim 9, wherein when the environment of use is indoors, the mixture of the ammonia nitrogen eliminating bacteriostat and the livestock excrement is irradiated by full illumination of an incandescent lamp.
CN201910925555.XA 2019-09-27 2019-09-27 Ammonia nitrogen eliminating bacteriostat Pending CN110606574A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116083495A (en) * 2023-04-10 2023-05-09 西北农林科技大学深圳研究院 Method for relieving inhibition of anaerobic digestion ammonia nitrogen by utilizing saccharomycetes

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102718327A (en) * 2012-07-05 2012-10-10 浙江皇冠科技有限公司 Nano-biological water body remediation agent for aquaculture and preparation method thereof
CN106861419A (en) * 2017-04-05 2017-06-20 山东优普生物工程有限公司 A kind of microbial deodorant and preparation method thereof
CN106915828A (en) * 2017-04-05 2017-07-04 新疆金兰德泰环保科技有限公司 A kind of water remediation microbial inoculum and preparation method thereof
CN107445309A (en) * 2017-06-26 2017-12-08 安徽省黄淮兽药有限公司 A kind of improver of water quality for aquaculture and preparation method thereof
CN109293184A (en) * 2018-09-28 2019-02-01 邓州市汇海农业科技有限公司 A kind of pig house waste deodorant

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102718327A (en) * 2012-07-05 2012-10-10 浙江皇冠科技有限公司 Nano-biological water body remediation agent for aquaculture and preparation method thereof
CN106861419A (en) * 2017-04-05 2017-06-20 山东优普生物工程有限公司 A kind of microbial deodorant and preparation method thereof
CN106915828A (en) * 2017-04-05 2017-07-04 新疆金兰德泰环保科技有限公司 A kind of water remediation microbial inoculum and preparation method thereof
CN107445309A (en) * 2017-06-26 2017-12-08 安徽省黄淮兽药有限公司 A kind of improver of water quality for aquaculture and preparation method thereof
CN109293184A (en) * 2018-09-28 2019-02-01 邓州市汇海农业科技有限公司 A kind of pig house waste deodorant

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
王迎军著: "《生物医用陶瓷材料》", 31 October 2010, 华南理工大学出版社 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116083495A (en) * 2023-04-10 2023-05-09 西北农林科技大学深圳研究院 Method for relieving inhibition of anaerobic digestion ammonia nitrogen by utilizing saccharomycetes

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Application publication date: 20191224