Method for maintaining stability of water quality in pipe network by using effect of iron oxidizing and reducing bacteria in biological membrane
A water quality stability, biofilm technology, applied in chemical instruments and methods, biological water/sewage treatment, water/sludge/sewage treatment, etc. effect of operation
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specific Embodiment approach 1
[0016] Specific implementation mode 1: Research on the change of water quality in Tiancun pipeline network
[0017] Pass the sterilized water into the Tiancun pipe, so that the concentration of residual chlorine in the pipe network is 1.5-2.5mg / L. After different days, the Larsen index of the water quality is changed. The experimental results show that the turbidity of the pipe network outlet water is different under different Larsen index conditions. The change is not very big, and the turbidity is relatively low, which meets the requirements of water quality standards.
specific Embodiment approach 2
[0018] Specific implementation mode 2: Research on the change of water quality in the pipe network of Ganlu Garden
[0019] Pass the sterilized water into the manna garden pipe, so that the concentration of residual chlorine in the pipe network is 1.5-2.5mg / L. After different days, the Larsen index of the water quality is changed. The experimental results show that the turbidity of the pipe network outlet water in the first 50 days is very large , "yellow water" is prone to occur. After 50 days, the turbidity of the pipe network outlet water does not change much under different Larsen index conditions, and the pipe network outlet water is relatively stable.
specific Embodiment approach 3
[0020] Specific implementation mode three: Characterization of biofilms in different pipe networks
[0021] DNA extraction, gene amplification and denaturing gradient gel electrophoresis (PCR-DGGE) analysis were performed on the biofilms formed by the Tiancun pipes without yellow water and the manna garden pipes with yellow water. Because the iron-oxidizing bacteria in the biofilm are the dominant bacteria, the iron-oxidizing bacteria are likely to cause the release of iron ions, and the turbidity of the pipe network effluent changes greatly with the change of the influent Larsen index. After increasing the amount of residual chlorine entering the pipe network, the pipe network The structure of the biofilm has changed, and iron-reducing bacteria have appeared, and they have become the dominant bacteria, which is the redox cycle environment for the formation of iron in the corrosion products, so it can inhibit the corrosion of the pipe network and reduce the impact of the Larsen...
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