Sewage treatment method

A sewage treatment and sewage technology, applied in water/sewage treatment, neutralized water/sewage treatment, reductive water/sewage treatment, etc., can solve the problem of electrode life not exceeding 2 years, low market acceptance, not exceeding 50%, etc. to improve the biodegradability, increase the degree of mineralization, and reduce the impact

A sewage treatment and sewage technology, applied in water/sewage treatment, neutralized water/sewage treatment, reductive water/sewage treatment, etc., can solve the problem of electrode life not exceeding 2 years, low market acceptance, not exceeding 50%, etc. to improve the biodegradability, increase the degree of mineralization, and reduce the impact

CN112047539APending Publication Date: 2020-12-08KUNSHAN MAYMUSE ENVIRONMENTAL TECH

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  • Sewage treatment method

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0021] Step 1. Use BDD electrodes to pretreat sewage, and the current density of BDD electrodes is 500A / square meter;

[0022] Step 2. Add ferrous sulfate as a flocculant with an addition amount of 0.2g / ton of water into the flocculation tank. When adding ferrous sulfate, add a small amount of alkali to adjust the pH to a suitable pH for the subsequent biochemical process. The sewage is pretreated Then flow into the flocculation tank and carry out flocculation treatment;

[0023] Step 3. The sewage is treated by biochemical process.

Embodiment 2

[0025] In embodiment 2, step 1 is adjusted, and the BDD electrode is adjusted to a graphene electrode, and the others are consistent with embodiment 1.

Embodiment 3

[0027] Embodiment 3 is adjusted for step 2, and the add-on of ferrous sulfate is adjusted to 0.5g / ton of water, and others are all consistent with embodiment 1.

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Abstract

The invention discloses a sewage treatment method. The method comprises the following steps: step 1, pretreating sewage by adopting an electrode; step 2, performing flocculation treatment in a flocculation tank by adopting ferrous sulfate as a flocculating agent; and step 3, treating by adopting a biochemical process. The method has the beneficial effects that the BDD electrode or the graphene electrode is used for pretreatment so that COD in the sewage is reduced, organic matters which are difficult to biodegrade are decomposed into small molecular organic matters, organic nitrogen is converted into inorganic nitrogen, and organic phosphorus is converted into inorganic phosphorus, the biodegradability of the sewage is greatly improved, the mineralization degree of pollutants in the sewageis improved, and subsequent flocculation treatment is facilitated; part of pollutants can be removed through flocculation treatment, the pollutants can react with residual active oxygen of electrooxidation, and the influence on the subsequent biochemical process is reduced. The sewage treatment method is easy to operate and can be used for effectively treating sewage.

Description

technical field [0001] The invention relates to the technical field of sewage treatment, in particular to a sewage treatment method. Background technique [0002] With the rapid development of economy and society and the gradual improvement of people's quality of life, the discharge of industrial wastewater and domestic wastewater is increasing day by day. Water pollution seriously endangers the health and life of people and animals, and seriously threatens human production, life and ecology. Balance, for sewage that is difficult to biodegrade, advanced oxidation is generally used as pretreatment. Advanced oxidation includes Fenton and ozone electrooxidation. The Fenton process needs to add a large amount of ferrous sulfate and hydrogen peroxide, and the process produces a large amount of solid waste. However, the oxidation ability of ozone is too weak, generally only 20mg / L of COD can be reduced, and the biodegradability of sewage is not greatly improved. Electrooxidatio...

Claims

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Application Information

Patent Timeline
08 Dec 2020
Publication
CN112047539A
IPC
C02F9/06; C02F101/30; C02F101/38
CPC
C02F9/00; C02F1/46109; C02F2001/46133; C02F1/5236; C02F1/70; C02F1/66; C02F2101/38; C02F2101/30
Inventors
左卫雄; 刘雅妮