Method for controlling growth of microcystis aeruginosa through combination of copper salt and chloramine
A technology of Microcystis aeruginosa and chloramine, which is applied in the field of drinking water treatment, can solve the problems of high operating cost, large investment, and lack of relevant structures, etc., and achieves the advantages of simple engineering construction operation process, low cost, and good algae inhibition effect Effect
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Embodiment 1
[0020] Eutrophication pollution occurred in the water source of a water plant. The concentration of Microcystis aeruginosa cells reached 100,000 / ml, and the turbidity of raw water was 15 NTU. The flocculant used in the water plant was aluminum chloride. When there is no eutrophication pollution in the water source, the dosage of flocculant is 15 mg / L to achieve a good removal effect, and the filtration cycle of the filter is 24 hours. However, after the above-mentioned eutrophication pollution occurred in the water source, the dosage of flocculant was increased to 25 mg / L, and the treatment effect was still unsatisfactory. The removal rate is only 80%, and the filtration cycle of the filter is shortened to 22 hours.
[0021] Adopt the method of the present invention to strengthen algae removal to the above-mentioned water source polluted by eutrophication:
[0022] Step 1: mixing liquid chlorine and ammonium sulfate with water, dissolving under sufficient stirring to obtain a...
Embodiment 2
[0028] Eutrophic pollution occurred in the water source of a water plant, the concentration of algae cells reached 1 million / ml, the turbidity of raw water was 40 NTU, and the flocculant used in the water plant was aluminum sulfate. When there is no eutrophication pollution in the water source, the flocculant dosage is 20 mg / L (calculated as aluminum) to achieve a good removal effect, and the filtration cycle of the filter is 24 hours. However, after the above-mentioned eutrophication pollution occurred in the water source, the dosage of flocculant was increased to 30 mg / L, and the treatment effect was still unsatisfactory. Only 70%, the filter cycle is shortened to 18 hours.
[0029] Adopt the method of the present invention to strengthen algae removal to the above-mentioned water source polluted by eutrophication:
[0030] Step 1: mix calcium hypochlorite and ammonium chloride with water, dissolve under sufficient stirring, and obtain an aqueous solution of calcium hypochlo...
Embodiment 3
[0036] Eutrophication pollution occurred in the water source of a water plant. The concentration of Microcystis aeruginosa growth cells reached 5 million / ml, and the turbidity of raw water was 200 NTU. The flocculant used in the water plant was polyaluminum chloride. When eutrophication pollution does not occur, a good removal effect can be achieved with a flocculant dosage of 25 mg / L (calculated as aluminum), and a filtration cycle of 24 hours. However, after the occurrence of eutrophication pollution, the dosage of flocculant was increased to 50 mg / L, and the treatment effect was still unsatisfactory. The turbidity of the water after sinking and filtration increased, and the removal rate of algae cells after sinking was only 40%. , The filter cycle is shortened to 15 hours.
[0037] Adopt the method of the present invention to strengthen algae removal to the above-mentioned water source polluted by eutrophication:
[0038] Step 1: Mix sodium hypochlorite and ammonium sulfate ...
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