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Method for controlling sludge expansion in biological pool and sewage treatment method

A sewage treatment method and sludge expansion technology, which are applied in biological water/sewage treatment, water/sludge/sewage treatment, and adjustment methods of biological treatment, etc. The effect of good treatment effect, fast settling speed and high microbial activity

Active Publication Date: 2020-09-25
北京恩菲环保技术有限公司
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

[0004] The main purpose of the present invention is to provide a method for controlling the expansion of biological pool sludge and a sewage treatment method, so as to solve the technical problem in the prior art that the sludge expansion of biological pools leads to the difficulty of mud-water separation and affects the quality of effluent water

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  • Method for controlling sludge expansion in biological pool and sewage treatment method
  • Method for controlling sludge expansion in biological pool and sewage treatment method
  • Method for controlling sludge expansion in biological pool and sewage treatment method

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Experimental program
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Effect test

Embodiment 1

[0045] A sewage treatment plant has a daily sewage treatment capacity of 30,000 tons per day, and undertakes the industrial wastewater treatment of 21 printing and dyeing enterprises in the area. The plant adopts a multi-stage treatment process of pretreatment + activated sludge method + advanced treatment. Influent water quality: CODcr is 940mg / L, BOD 5 The SS is 210mg / L, the SS is 432mg / L, the color is 256 times, and the pH value is 7.9. The effluent water quality is: CODcr is 45mg / L, BOD 5 It is 1mg / L, SS is 5mg / L, the chromaticity is 30 times, and the pH value is 7.0. During operation, sludge bulking occurred in a biological pool of a certain line, and the sludge volume index rose to 250ml / g. The results of sludge microscopy showed that a large number of filamentous bacteria grew and reproduced, causing sludge bulking.

[0046] The method steps for rapid control of sludge bulking and improvement of sludge settleability are as follows:

[0047] (1) Choose a particle size...

Embodiment 2

[0054] A sewage treatment plant has a daily sewage treatment capacity of 10,000 tons per day, and the treated sewage is printing and dyeing industrial wastewater. The plant adopts a multi-stage treatment process of pretreatment + activated sludge method + advanced treatment. Influent water quality: CODcr is 629mg / L, BOD 5 113mg / L, SS 264mg / L, effluent water quality: CODcr 52mg / L, BOD 5 2mg / L, SS 5mg / L. During the operation, a line of biological pools had sludge swelling caused by filamentous bacteria, and the sludge volume index was 200ml / g.

[0055] The method steps for rapid control of sludge bulking and improvement of sludge settleability are as follows:

[0056] (1) Choose a particle size of 150 mesh and a bulk density of 0.55g / cm 3 wood activated carbon;

[0057] (2) According to the above-mentioned sludge volume index 200ml / g, the activated carbon dosing ratio R is determined to be: activated carbon concentration: sludge concentration=1:3;

[0058] (3) According to...

Embodiment 3

[0063] A paper-making enterprise produces 20,000 tons of sewage per day, and the sewage treatment process of the enterprise adopts a multi-stage treatment process of pretreatment + activated sludge method + advanced treatment. Influent water quality: CODcr is 1700mg / L, BOD 5 It is 530mg / L, SS is 823mg / L, and the pH value is 8.2. The effluent water quality is: CODcr is 86mg / L, BOD 5 It is 13mg / L, SS is 15mg / L, and the pH value is 7.3. During the operation, sludge bulking occurred in the biological pool, and the sludge volume index increased to 150ml / g. The results of sludge microscopy showed that the growth and reproduction of filamentous bacteria caused sludge bulking.

[0064] The method steps for rapid control of sludge bulking and improvement of sludge settleability are as follows:

[0065] (1) Choose a particle size of 300 mesh and a bulk density of 0.5g / cm 3 wood activated carbon;

[0066] (2) According to the above-mentioned sludge volume index of 150ml / g, the activ...

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Abstract

The invention provides a method for controlling sludge bulking in a biological tank and a sewage treatment method. The method for controlling sludge bulking in the biological tank comprises the step of adding activated carbon into the biological tank so as to control the sludge bulking in the biological tank. According to the method, the activated carbon is added into the biological tank, the sludge bulking volume is controlled under the condition that the activity of microorganisms in the sludge is not damaged, the settling rate is high, and the biochemical treatment effect of the biological tank is excellent (the microbial activity is high). Moreover, compared with the prior art, the using method for using the activated carbon in sewage treatment is different. The method in the prior art is that the activated carbon is added into water discharged after secondary settlement, and pollutants in the water are adsorbed and filtered by utilizing strong adsorptive property of the activated carbon, instead of taking the activated carbon as a sludge gathering center to reduce the bulking volume.

Description

technical field [0001] The invention relates to the field of water pollution control, in particular to a method for controlling sludge expansion in biological pools and a sewage treatment method. Background technique [0002] Activated sludge method is currently the most widely used method in the field of water treatment, accounting for more than 95% of urban sewage and about 50% of industrial wastewater treatment. Sludge bulking has a high occurrence rate and is difficult to control in the operation and management of sewage plants, which has plagued the stable operation of sewage treatment plants for a long time. At present, the main control methods for sludge bulking include: adding various agents such as flocculants, fungicides, and lime. Or set a biological selector at the front end of the system to improve process control conditions, etc. These methods have the disadvantages of easy destruction of microbial activity, slow effect and long cycle, making it difficult to ...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): C02F3/12
CPCC02F3/006C02F3/12Y02W10/10
Inventor 张强卢东昱吴运松张鑫骆平
Owner 北京恩菲环保技术有限公司