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Achromobacter xylosoxidans strain for biological denitrificaion and application thereof

An achromobacter, biological denitrification technology, applied in the field of biological denitrification, can solve problems such as long process, achieve the effect of broad application prospect, simplified process flow and good social benefit

Inactive Publication Date: 2011-05-04
PEKING UNIV
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

The biological denitrification process developed according to the traditional biological denitrification theory usually carries out nitrification and denitrification in the aerobic zone and anoxic zone respectively, forming a graded nitrification and denitrification process, so the nitrification pool and the denitrification pool must be built separately, so that There are many deficiencies in the graded nitrification and denitrification process: (1) lengthy process
However, there are few reports on bacteria capable of both heterotrophic nitrification and aerobic denitrification, and the practical application of such special bacteria in wastewater denitrification treatment is still blank.

Method used

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  • Achromobacter xylosoxidans strain for biological denitrificaion and application thereof
  • Achromobacter xylosoxidans strain for biological denitrificaion and application thereof
  • Achromobacter xylosoxidans strain for biological denitrificaion and application thereof

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0037] Example 1. Obtainment of strain GAD3 with heterotrophic nitrification-aerobic denitrification performance and biological denitrification experiment

[0038] 1. Separation and purification method of strain GAD3 with heterotrophic nitrification-aerobic denitrification performance

[0039] The method has the following steps:

[0040] 1) Take out sludge samples from the combined treatment system of landfill leachate in Shenzhen Buji landfill;

[0041] 2) Inoculate into a 500mL Erlenmeyer flask containing 100mL enriched culture solution: each L contains 0.95g NaNO 3 , 0.7g peptone, 0.5g beef extract, 0.15g urea, 0.04g NaCl, 0.15g KH 2 PO 4 , 0.02g KCl, 0.03g MgSO 4 ·7H 2 O, 0.20g CaCl 2 ·2H 2 O, pH 7.0-7.5;

[0042] 3) Wrap the mouth of the bottle with gauze, and culture for 4 days at 30°C and 140 rpm shaker;

[0043] 4) Take the bacterial solution in the shake flask as the source of bacterial seed, take out 10mL and inoculate it into a fresh conical flask containing 150mL enriched cul...

Embodiment 2

[0062] Example 2. Biological Denitrification Experiment

[0063] The strain GAD3 and its bacterial suspension prepared by the method provided in Example 1 were used for biological denitrification experiments.

[0064] 1. Take ammonia nitrogen (NH 4 + -N) Biological nitrogen removal experiment with nitrogen source

[0065] Take 5mL of the prepared GAD3 bacterial suspension and add it to three culture flasks containing 95ml test medium (each L medium contains 1.52g NH 4 Cl, 1.0g KH 2 PO 4 , 0.06g FeSO 4 ·7H 2 O, 0.2gCaCl 2 ·2H 2 O, 1.0g MgSO 4 ·7H 2 O, 8.1g sodium citrate, pH 8.0), sealed with 9 layers of gauze, 15°C, 160rpm (rotation radius 15mm) shake culture in a shaker. The medium without bacterial suspension was subjected to the experiment under the same conditions as a blank control. The reaction solution was taken the next day and centrifuged at 4000 rpm for 10 min. The supernatant was taken to determine the concentration of various nitrogen-containing compounds.

[0066] The re...

Embodiment 3

[0071] Example 3. Experiment of biological denitrification conditions

[0072] The strain GAD3 and its bacterial suspension prepared by the method provided in Example 1 were subjected to biological denitrification condition experiments.

[0073] 1. Take ammonia nitrogen (NH 4 + -N) Biological denitrification condition experiment with nitrogen source

[0074] Take 5mL of the prepared GAD3 bacterial suspension and add it to 9 culture flasks containing 95ml test medium (each L medium contains 0.57g NH 4 Cl, 1.0g KH 2 PO 4 , 0.06g FeSO 4 ·7H 2 O, 0.2gCaCl 2 ·2H 2 O, 1.0g MgSO 4 ·7H 2 O, 7.72g anhydrous sodium acetate), the initial pH is 5.0, 6.0, 7.0, 8.0, 9.0, 10.0, 11.0, respectively. Seal with 9 layers of gauze, shake culture in a shaker at 40°C and 160 rpm (rotation radius of 15 mm). The medium without bacterial suspension was used as a blank control under the same conditions. After culturing for 24 h, take the reaction solution in the shake flask, centrifuge at 4000 rpm for 10 min...

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Abstract

The invention discloses an achromobacter xylosoxidans strain for biological denitrificaion and application thereof. The achromobacter xylosoxidans strain GAD3 is preserved in China General Microbiological Culture Collection Center (CGMCC for short) with preservation number CGMCC No. 2964 in March 19th, 2009. The strain is added to nitrogenous effluent with 2 to 6mg / L of dissolved oxygen to realizebiological denitrificaion. The strain not only has the capability of heterotrophic nitrification, but also has the capability of aerobic denitrification. In the process of treating the nitrogenous effluent, only one aerobic stage is needed, the denitrification efficiency is high, and the operation is convenient and quick; and compared with the conventional biological denitrification process, theapplication has huge economic benefits.

Description

Technical field [0001] The invention relates to the field of biological denitrification, in particular to a strain of Achromobacter xylosoxidans for biological denitrification and its application. Background technique [0002] The main forms of nitrogen in wastewater are molecular nitrogen, organic nitrogen, ammonia nitrogen, nitrite nitrogen, nitrate nitrogen, and part of nitrogen that exists in hydrogen sulfide and cyanide. Due to the toxic effects of ammonia nitrogen, the carcinogenic effects of nitrates, and the acidification and eutrophication effects of nitrogen compounds on ecosystems, rivers, lakes, and offshore oceans, sewage treatment technologies that economically and efficiently remove nitrogen from water have become water pollution Research focus and hot spots in the field of control. [0003] Among the various denitrification methods currently used, biological denitrification is still the main method of wastewater denitrification treatment. The traditional wastewate...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): C12N1/20C02F3/30C02F3/34C02F101/16C12R1/025
Inventor 倪晋仁陈倩
Owner PEKING UNIV