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Heterotrophic nitrification-aerobic denitrification compound microorganism preparation and preparation method thereof

A composite microorganism and aerobic denitrification technology, which is applied in the field of heterotrophic nitrification-aerobic denitrification composite microbial preparation and its preparation, can solve the problems of unfavorable and rapid control of ammonia nitrogen content in water, many process links and high treatment costs, and achieves pH The effect of stable value, cost reduction and high ammonia nitrogen removal rate

Inactive Publication Date: 2018-12-21
DINGZHENG XINXING BIOTECH TIANJIN
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

The above-mentioned denitrification process has many technical links, high processing cost and long time, which is not conducive to quickly controlling the ammonia nitrogen content of the water body. In the case of post-type denitrification, due to the lack of organic matter in the mixed liquid, it is generally necessary to manually add carbon sources.

Method used

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  • Heterotrophic nitrification-aerobic denitrification compound microorganism preparation and preparation method thereof
  • Heterotrophic nitrification-aerobic denitrification compound microorganism preparation and preparation method thereof
  • Heterotrophic nitrification-aerobic denitrification compound microorganism preparation and preparation method thereof

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0039] 1. Mix Vibrio alginolyticus and Pseudomonas aeruginosa in a ratio of 1:2.31;

[0040] 2. The medium composition is:

[0041] The medium formula is (g / L): Tryptone 10; Yeast extract 5; NaCl 10; NH 4 Cl 0.5; sodium citrate 5.66; 50 mL of Vickers salt solution, seawater (NaCl 15) with a salinity of 15‰, adjust the pH to 7.0.

[0042] Vickers salt solution (g / L): K 2 HPO 4 5.0; MgSO 4 ·7H 2 O 2.5; FeSO 4 ·7H 2 O 0.05; MnSO 4 ·4H 2 O0.05.

[0043] 3. Inoculate the mixture of step 1 at 5% of the volume of the medium, and cultivate it at a temperature of 25 degrees Celsius and a rotation speed of 100 to 130 revolutions per minute, with a pH of 7.0 to 7.5;

[0044] 4. Detect the OD value of the culture after culturing for 20 hours. When the OD value reaches 2.15±0.02, the fermentation is completed.

Embodiment 2

[0046] 1. Mix Vibrio alginolyticus and Pseudomonas aeruginosa in a ratio of 1:5.52;

[0047] 2. The medium composition is:

[0048] The medium formula is (g / L): Tryptone 10; Yeast extract 5; NaCl 10; NH 4 Cl 0.5; sodium citrate 5.66; 50 mL of Vickers salt solution, seawater (NaCl 15) with a salinity of 15‰, adjust the pH to 7.0.

[0049] Vickers salt solution (g / L): K 2 HPO 4 5.0; MgSO 4 ·7H 2 O 2.5; FeSO 4 ·7H 2 O 0.05; MnSO 4 ·4H 2 O0.05.

[0050] 3. Inoculate the mixture of step 1 at 1% of the volume of the culture medium, and cultivate it at a temperature of 35 degrees Celsius and a rotation speed of 100 to 130 revolutions per minute, with a pH of 7.0 to 7.5;

[0051] 4. Detect the OD value of the culture after 30 hours of incubation. When the OD value reaches 2.15±0.02, the fermentation is completed.

Embodiment 3

[0053] 1. Mix Vibrio alginolyticus and Pseudomonas aeruginosa in a ratio of 1:3;

[0054] 2. The medium composition is:

[0055] The medium formula is (g / L): Tryptone 10; Yeast extract 5; NaCl 10; NH 4 Cl 0.5; sodium citrate 5.66; 50 mL of Vickers salt solution, seawater (NaCl 15) with a salinity of 15‰, adjust the pH to 7.0.

[0056] Vickers salt solution (g / L): K 2 HPO 4 5.0; MgSO 4 ·7H 2 O 2.5; FeSO 4 ·7H 2 O 0.05; MnSO 4 ·4H 2 O0.05.

[0057] 3. Inoculate the mixture of step 1 at 3% of the volume of the medium, and cultivate it at a temperature of 30 degrees Celsius and a rotation speed of 100 to 130 revolutions per minute, with a pH of 7.0 to 7.5;

[0058] 4. Detect the OD value of the culture after 30 hours of incubation. When the OD value reaches 2.15±0.02, the fermentation is completed.

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Abstract

The invention relates to a heterotrophic nitrification-aerobic denitrification compound microorganism preparation. The compound microorganism preparation is characterized in that vibrio alginolyticusand pseudomonas aeruginosa are utilized as raw materials, and the two raw materials are mixed and fermented to obtain a finished product. According to the compound microorganism preparation disclosedby the invention, the vibrio alginolyticus HA2 and the pseudomonas aeruginosa YY24 are utilized as the raw materials, and the two bacterial raw materials are mixed and fermented to obtain the finishedproduct; when being used, the compound microorganism preparation is directly added into an aerating tank according to the proportion; nitration and denitrification processes are simultaneously performed, the two bacterial raw materials can mutually provide a part of nutritional substances required by growth, and special and expensive inducing matter is not needed in culture; furthermore, conditions are extremely simple, and industrialized production cost is greatly reduced; in addition, nitration reaction can limit a water body pH value increased by denitrification reaction and can make the water body pH value relatively stable; furthermore, a removal rate for ammonium and nitrogen in a water body is high, action time is short, and ecological activities of fish, shrimps, plants and the like are prevented from being affected; thus, the compound microorganism preparation can be applied to water bodies with exceeding nitrogen contents like ordinary fresh water earthern ponds, factorizedfresh water / seawater workshops, domestic sewage, weak-acid water bodies, industrial wastewater and the like.

Description

Technical field [0001] The invention relates to the technical field of three-state nitrogen treatment in water bodies, in particular to a heterotrophic nitrification-aerobic denitrification compound microbial preparation and a preparation method thereof. Background technique [0002] There are three states of N element in water: nitrate nitrogen (in the form of nitrate), nitrite (nitrite) and ammonium (ammonium). These substances have a certain influence on the growth and development of aquaculture in the water. Once it reaches a certain concentration, it will accumulate in the cultured objects, indirectly affect human health, and even cause the death of the cultured objects. [0003] Traditional water treatment theory believes that the removal of ammonia nitrogen is achieved through two independent processes of nitrification and denitrification. Due to the different requirements for environmental conditions, these two processes cannot occur simultaneously, but can only be carried ...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): C12N1/20C02F3/02C02F3/34C12R1/385C12R1/63C02F101/16
CPCC12N1/20C02F3/02C02F3/34C02F2101/166C02F2101/163C02F2101/16Y02W10/10
Inventor 陈成勋王立红刘兴刘鼎阔孙蒙蒙董惠峰李连星李源
Owner DINGZHENG XINXING BIOTECH TIANJIN