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A method of anaerobic-aerobic deep coupling treatment of organic wastewater with high solid content

A high solid content, organic wastewater technology, applied in aerobic and anaerobic process treatment, water treatment parameter control, chemical instruments and methods, etc., can solve problems such as lack, lethal cell damage, anaerobic reaction failure, etc., to achieve Improved impact load resistance, light suppression, and improved biogas output

Active Publication Date: 2022-04-19
恩格拜(武汉)生态科技有限公司
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  • Claims
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AI Technical Summary

Problems solved by technology

[0005] DO (dissolved oxygen in water) problem: the aerobic process generally requires a large amount of oxygen. For example, the dissolved oxygen in the aerobic section of the A / O process is controlled above 2.0mg / L, while in the anaerobic reaction, especially the methanogenic stage, due to Methanogens lack superoxide dismutase and are sensitive to O 2 very sensitive
If the effluent of the traditional aerobic biochemical process is directly recycled to the anaerobic unit, a large amount of O 2 It will interact with some active groups in the cells of methanogens, leading to the disintegration of important enzyme systems; at the same time, O 2 The superoxide anion free radicals produced will also cause lethal damage to cells, which will eventually lead to the failure of anaerobic reactions;
[0006] Nitrate nitrogen problem: It is generally believed that the anaerobic environment is a water body environment where there is no nitrate nitrogen or a very small amount, but most aerobic processes can only do a good job in the conversion process of ammonia nitrogen to nitrate nitrogen, but cannot complete the conversion process of nitrate nitrogen to nitrogen conversion
That is to say, once the aerobic effluent returns to the anaerobic unit, it will carry a large amount of nitrate nitrogen, directly destroying the anaerobic environment, so that the heterotrophic bacteria in the reactor become the dominant species, seriously affecting the anaerobic reaction process, and even failure of anaerobic reaction
[0007] In addition, for sewage with high suspended solids (solid content > 3%), after the anaerobic reaction, the fine particles and suspended matter in the mixed solution are anaerobic products, which will be mixed with other reactants and good after directly entering the aerobic biochemical tank. Aerobic and facultative species compete for O 2 , resulting in insufficient oxygen supply in the biochemical pool, destroying the aerobic environment, thereby affecting the efficiency of the aerobic reaction, therefore, it is necessary to reduce the content of suspended matter in the aerobic influent

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  • A method of anaerobic-aerobic deep coupling treatment of organic wastewater with high solid content
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  • A method of anaerobic-aerobic deep coupling treatment of organic wastewater with high solid content

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application example 1

[0048] A pig farm has 13,500 sows and 150,000 fattening pigs. The manure cleaning method is water-soaked manure mode. The manure and sewage discharge Q=2000m³ / d. Raw water indicators: COD≤18000mg / L, TKN≤1300mg / L, TS<4% , require effluent COD<150mg / L, ammonia nitrogen<100mg / L, and have energy utilization requirements. According to the project requirements, the following process flow is designed: solid-liquid separation unit, anaerobic reaction unit and aerobic reaction unit. The solid-liquid separation unit includes grille, slag separation tank and solid-liquid separator. The anaerobic treatment unit adopts IC reactor, and the aerobic treatment unit adopts synchronous nitrification and denitrification process.

[0049] S1: Feces and sewage pass through the grille, slag separation tank, and solid-liquid separator in sequence, and the floating matter, small particles, and suspended matter in the sewage are intercepted and separated, and after collection, they are composted to obt...

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Abstract

A method for anaerobic-aerobic deep coupling treatment of high solid content organic wastewater includes: after the organic waste is crushed and screened, the filtered slurry is put into an anaerobic reaction unit, and biogas and biogas slurry are obtained by anaerobic fermentation; The oxygen effluent is passed into the solid-liquid separation unit for solid-liquid separation, and the separated biogas residue is returned to the anaerobic reaction unit through the sludge return pump; the separated biogas slurry enters the aerobic reaction unit, and undergoes a synchronous nitrification and denitrification process to remove nitrogen; Part of the effluent from the aerobic reaction unit flows back to the anaerobic reaction unit, where it is fully diluted and mixed with the original slurry of organic waste for anaerobic reaction, and the other part of the effluent enters the next treatment process or discharges up to the standard. The anaerobic effluent of the present invention enters the solid-liquid separation unit to separate suspended matter, and the effluent enters the aerobic unit to control the DO value in the water body of the aerobic unit to complete denitrification. After that, the aerobic effluent controls the reflux ratio and returns to the anaerobic unit again. Circular reaction, improve anaerobic biogas production rate, and at the same time, the quality of aerobic effluent is higher.

Description

technical field [0001] The invention relates to a method for anaerobic-aerobic deep coupling treatment of organic wastewater with high solid content, and belongs to the technical field of sewage treatment. Background technique [0002] Anaerobic reactors are generally preferred for waste water treatment and resource utilization. However, since the reactants often contain a large amount of nitrogen-containing substances, during the anaerobic fermentation process, a large amount of protein will be transformed and decomposed, and a large amount of free ammonia nitrogen will be released, resulting in ammonia nitrogen. Accumulated, the ammonia nitrogen concentration often reaches above 2000mg / L. According to research, an important nutritional factor affecting the growth of methanogens is ammonia nitrogen. When the concentration of ammonia nitrogen is 50-200 mg / L, it is conducive to the anaerobic reaction; but when the concentration of ammonia nitrogen reaches 2000 mg / L or more, i...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): C02F3/30
CPCC02F3/302C02F3/307C02F2101/38C02F2209/08
Inventor 李明维克·恩格拜鄢紫
Owner 恩格拜(武汉)生态科技有限公司
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