Device for enriching anaerobic ammonia-oxidizing bacteria and method for treating wastewater by using the device
A technology for enriching red bacteria and treating wastewater, which is applied in the adjustment methods of biological treatment, water treatment parameter control, chemical instruments and methods, etc. , slow growth of anammox bacteria, etc., to achieve the effect of shortening sludge retention time, shortening hydraulic retention time, and increasing holding capacity
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[0023] DETAILED DESCRIPTION a: an apparatus according to the present embodiment, the enrichment of bacteria were used, including reaction vessel 10, and the gas generation rate detection means output 3, an air pump 5, aerator 6, 7 stirrer, a filler means 9, the end concentration measuring device 11, PLC 12 and the motor 13;
[0024] The reactor is provided with a water inlet port to add nutrients and 4, the side wall 2 is provided with an outlet 10 on the sidewalls of the lower portion of the reaction vessel upper portion of the tank 10; the signal receiving end of said gas production rate detecting means and generating 3 sensing probe and the composition, and the signal receiving terminal connected to sensing probe, the sensing probe is disposed above the reaction can 10; inside the reaction tank 10 is provided with a stirrer 7, the motor 13 is connected through a coupling 7 with a stirrer ; the lower tank 10 is provided in the reaction with substrate concentration measuring devi...
Example Embodiment
[0025] DETAILED Embodiment 2: Embodiment of the present embodiment and a particular embodiment is different: the filler means 9 is provided with a filler, and the filler is a ceramic foam, said ceramic foam with a volume ratio of 2: 1 .
[0026] The foam having a strong adhesive, can be adsorbed on the surface of the ceramic; ceramic developed pore structure, it can be inclusive of foam adhered to each other both increases friction, to facilitate the interception of red bacteria, such bacteria capable of adsorbing red and the ceramic foam surface, while reducing the influence of both the synergistic effect of aeration during agitation to form a granular sludge anammox bacteria and promote red enriched bacteria.
[0027] The other steps are the same as a specific embodiment.
Example Embodiment
[0028] DETAILED Embodiment 3: Embodiment of the present embodiment and the exemplary embodiment is one or two different points: at the outlet 2 is provided with a water filter, pore size of the membrane effluent is 0.45μm.
[0029] Other specific embodiments of a step or two identical.
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