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Composite strain biological fluid bed membrane method and anaerobic filler preparation method

A compound strain, fluidized bed technology, applied in anaerobic digestion treatment, chemical instruments and methods, biological water/sewage treatment, etc., to achieve the effect of promoting rapid establishment, releasing inhibition, and promoting step-by-step diffusion

Active Publication Date: 2020-05-19
浙江永续环境工程有限公司
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

[0007] The purpose of the present invention is to provide a composite strain biofluidic bed film method and anaerobic filler preparation method with better use effect, to solve at least one technical problem in the prior art

Method used

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  • Composite strain biological fluid bed membrane method and anaerobic filler preparation method

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Embodiment 1

[0044] The present invention provides a biofluidized bed membrane method for composite strains. The biofluidized bed membrane method for composite strains includes the following steps: anaerobic tank treatment, anaerobic filler is arranged in the anaerobic tank, and the anaerobic 5% of the water mass in the filled anaerobic tank enters the anaerobic tank for treatment, and the treatment time is 24 hours; for the treatment in the first sedimentation tank, the sewage enters the first sedimentation tank for sedimentation treatment for 6 hours; for the treatment in the aerobic tank, the The aerobic tank is provided with aerobic filler, and the aerobic filler accounts for 5% of the water quality in the anaerobic tank, and the sewage enters the aerobic tank for treatment, and the treatment time is 12 hours; for the second sedimentation tank, the sewage enters Sediment in the second sedimentation tank for 6 hours.

[0045] The anaerobic filler includes a coated net, a middle material...

Embodiment 2

[0050] The present invention provides a biofluidized bed membrane method for composite strains. The biofluidized bed membrane method for composite strains includes the following steps: anaerobic tank treatment, anaerobic filler is arranged in the anaerobic tank, and the anaerobic 20% of the water quality in the filled anaerobic tank enters the anaerobic tank for treatment, and the treatment time is 14 hours; for the treatment in the first sedimentation tank, the sewage enters the first sedimentation tank for sedimentation treatment for 3 hours; for the treatment in the aerobic tank, the The aerobic tank is provided with aerobic filler, and the aerobic filler accounts for 20% of the water quality in the anaerobic tank, and the sewage enters the aerobic tank for treatment, and the treatment time is 7 hours; for the second sedimentation tank, the sewage enters Sediment in the second sedimentation tank for 3 hours.

[0051] The anaerobic filler includes a coated net, a middle mate...

Embodiment 3

[0056] The present invention provides a biofluidized bed membrane method for composite strains. The biofluidized bed membrane method for composite strains includes the following steps: anaerobic tank treatment, anaerobic filler is arranged in the anaerobic tank, and the anaerobic 30% of the water quality in the filled anaerobic tank enters the anaerobic tank for treatment, and the treatment time is 4 hours; for the treatment in the first sedimentation tank, the sewage enters the first sedimentation tank for sedimentation treatment for 1 hour; for the treatment in the aerobic tank, the The aerobic tank is provided with aerobic filler, and the aerobic filler accounts for 30% of the water quality in the anaerobic tank, and the sewage enters the aerobic tank for treatment, and the treatment time is 2 hours; for the second sedimentation tank, the sewage enters Sediment in the second sedimentation tank for 1 hour.

[0057] The anaerobic filler includes a coated net, a middle materia...

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Abstract

The invention provides a composite strain biological fluidized bed membrane method which comprises the following steps: anaerobic tank treatment: an anaerobic filler is arranged in an anaerobic tank,sewage accounting for 5-30% of the mass of a water body in the anaerobic tank is introduced into the anaerobic tank to be treated, and the treatment time is 4-24 hours; treatmentin a first sedimentation tank: the sewage is introduced into the first sedimentation tank to be subjected to sedimentation treatment for 1-6 hours; treatment in an aerobic tank: anaerobic filler is arranged in the aerobictank, the aerobic filler accounts for 5-30% of the mass of the water body in the anaerobic tank, the sewage is introduced intothe aerobic tank to be treated, and the treatment time is 2-12 hours; treatment in a second sedimentation tank: the sewage is introduced intothe second sedimentation tank to be settled for 1-6 hours. The invention also provides a preparation method of the anaerobic filler.According to the method, an effective sheltering space can be provided for mixed strains, the propagation speed of the strains is increased, dominant bacterial colonies are established for the targetstrains in the sewage, and therefore the sewage purification rate is increased.

Description

technical field [0001] The invention relates to the technical field of sewage treatment, in particular to a compound bacterial species biological flow bed membrane method and an anaerobic filler preparation method. Background technique [0002] With the continuous acceleration of China's urbanization process, the urban population is also increasing, and the scale of the city is constantly expanding, which puts forward higher requirements for the supporting facilities of the city, especially for the supporting facilities of urban residents' domestic waste. Facilities, because they are urban sewage, have their own harmful properties and have the characteristics of long duration and high pollution degree, so timely and efficient urban sewage is a research hotspot in this field. [0003] For urban sewage, it has its own distinctive characteristics, that is, it contains a large amount of organic substances, such as starch, protein, oil, etc., and a large amount of inorganic subst...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): C02F9/14C02F3/30C02F3/28C02F3/34
CPCC02F9/00C02F3/308C02F3/2806C02F3/345C02F3/34C02F3/348C02F2209/44C02F2003/001Y02W10/10
Inventor 郑勇生言红红郑言
Owner 浙江永续环境工程有限公司
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