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Anaerobic-SBR-SACR combined deep denitrification system and process for high-ammonia-nitrogen sewage

A -SBR-SACR, deep denitrification technology, applied in the field of anaerobic-SBR-SACR combined high ammonia nitrogen sewage deep denitrification system, can solve the problem of high process treatment cost, achieve low upgrade cost and reduce treatment cost. Effect

Active Publication Date: 2020-01-17
SHANDONG JIANZHU UNIV
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

The traditional SBR process generally adopts post-denitrification method to achieve deep denitrification of wastewater, but it needs to add carbon source, and the process treatment cost is high

Method used

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  • Anaerobic-SBR-SACR combined deep denitrification system and process for high-ammonia-nitrogen sewage
  • Anaerobic-SBR-SACR combined deep denitrification system and process for high-ammonia-nitrogen sewage
  • Anaerobic-SBR-SACR combined deep denitrification system and process for high-ammonia-nitrogen sewage

Examples

Experimental program
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Effect test

Embodiment 1

[0033] Example 1: An anaerobic-SBR-SACR combined deep denitrification system for high ammonia nitrogen sewage

[0034] Such as figure 1 As shown, an anaerobic-SBR-SACR combined high-ammonia-nitrogen sewage deep denitrification system includes a regulating tank, anaerobic reactor, SBR inlet tank, SBR reactor, intermediate tank and SACR reactor connected in sequence through pipelines The outlet end of the regulating pool is connected with the inlet end of the intermediate pool through a pipeline; the pipeline is provided with a water pump for regulating the flow rate; the intermediate pool is provided with water quality detection equipment; the SACR reactor is provided with a PH detector , DO detector, ORP detector, aeration equipment and agitator; also includes a PLC controller, the PLC controller is respectively connected with water quality testing equipment, PH detector, DO detector, ORP detector, aeration equipment and stirring device communication connection.

[0035] In ...

Embodiment 2

[0038] Example 2: An anaerobic-SBR-SACR combined deep denitrification process for high-ammonia nitrogen sewage

[0039] The process in this example is based on the system in Example 1, and the anaerobic reactor is a UASB reactor; the volume of the SBR inlet pool=the daily output of sewage×0.5 m 3 ; Volume of SBR reactor = (total nitrogen concentration value of high ammonia nitrogen sewage raw water / 50×30×hourly sewage production value) m 3 ; The unit of total nitrogen concentration in high ammonia nitrogen sewage raw water is mg / L, and the unit of sewage output per hour is m 3 ;SACR volume = (total nitrogen concentration value of high ammonia nitrogen sewage raw water / 50×20×hourly sewage production value) m 3 ; The unit of total nitrogen concentration in high ammonia nitrogen sewage raw water is mg / L, and the unit of sewage output per hour is m 3 .

[0040] An anaerobic-SBR-SACR combined high-ammonia-nitrogen sewage deep denitrification process, comprising the following ste...

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Abstract

The invention provides an anaerobic-SBR-SACR combined deep denitrification system and process for high-ammonia-nitrogen sewage. According to the process, high-ammonia-nitrogen sewage firstly enters ananaerobic reactor for removal of most of organic matters; the effluent of the anaerobic reactor sequentially enters an SBR water inlet tank and an SBR reactor, and pre-denitrification and nitrification are carried out through the SBR to remove biochemical organic matters, ammonia nitrogen and a part of total nitrogen; the effluent of the SBR reactor enters an intermediate water tank; under the control of water quality detection equipment and a PLC, a part of raw water is introduced into the intermediate water tank to adjust the carbon-nitrogen ratio of the sewage; and then the effluent entersan SACR reactor. By utilizing the characteristics of denitrifying bacteria and by regulating and controlling the SACR reactor via a PH / DO / ORP detector and the PLC, the sewage is accurately subjectedto pre-denitrification / nitrification / endogenous denitrification, so deep denitrification is realized; meanwhile, an external carbon source is not needed, and the cost of the process is low; and for abuilt sewage treatment facility adopting an SBR process, the process with the above technical scheme can be implemented only by additionally arranging the intermediate water tank and the SACR reactor,so upgrading and reconstruction cost is low.

Description

technical field [0001] The invention relates to the technical field of sewage treatment, in particular to an anaerobic-SBR-SACR combined deep denitrification system and process for high ammonia nitrogen sewage. Background technique [0002] At present, with the strengthening of environmental protection awareness, the strengthening of environmental pollution control and the development of environmental protection technology, water pollution has been relatively effectively controlled initially. However, the standard discharge of high-ammonia-nitrogen wastewater common in industrial production is still an urgent problem. The problem. High ammonia nitrogen wastewater mainly comes from chemical fertilizer, petrochemical, aquaculture, garbage treatment and other industries. In terms of high ammonia nitrogen wastewater treatment, it is not only necessary to pursue the technical indicators of efficient denitrification, but also to consider reducing energy consumption, saving energy ...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): C02F9/14C02F101/16
CPCC02F3/1263C02F3/28C02F3/302C02F2001/007C02F2101/16C02F2209/005C02F2209/04C02F2209/06C02F2209/22
Inventor 王凯武道吉谭凤训罗从伟成小翔李宏业田宇
Owner SHANDONG JIANZHU UNIV
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