Catalyst for alkaline hydrolysis of pyraclostrobin production wastewater, preparation method of catalyst and pretreatment method of pyraclostrobin production wastewater
A technology for pyraclostrobin and production wastewater, which is applied in catalyst activation/preparation, water/sewage treatment, neutralization water/sewage treatment, etc., can solve the problem that the pretreatment effect of pyraclostrobin production wastewater cannot be effectively improved, MVR multi-effect evaporation has problems such as high energy consumption, increased acid-base neutralization cost, etc., to achieve the effect of improving load stability, large number of active sites, and high use value
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Embodiment 1
[0035] A catalyst for alkaline hydrolysis of waste water produced by pyraclostrobin is obtained by curing a catalyst carrier, an iron-based metal catalyst, and sodium alginate through the crosslinking action of a crosslinking agent, wherein the catalyst carrier is modified biomass charcoal.
[0036] In this embodiment, the mass ratio of modified biochar, iron-based metal catalyst, and sodium alginate is 3:0.1:2.
[0037] In this example, the modified biochar is obtained by modifying the biochar through a micelle system, wherein the micelle system is obtained by mixing a rhamnolipid solution, a cationic chemical surfactant solution and a humic acid solution. The volume ratio of rhamnolipid solution, cationic chemical surfactant solution and humic acid solution is 1:5:14; the concentration of rhamnolipid in rhamnolipid solution is 80mmol / L; The cationic chemical surfactant is a quaternary ammonium salt surfactant (cetyltrimethylammonium bromide, CTAB), and the concentration is 8...
Embodiment 2
[0054] A catalyst for alkaline hydrolysis of pyraclostrobin production wastewater, which is basically the same as in Example 1, except that in Example 2, the iron-based metal catalyst is FeCl 2 4H 2 O crystals.
[0055] The catalyst in Example 2 was used to treat pyraclostrobin production wastewater, and the treatment conditions were the same as in Example 1. The verification results of biochemical experiments show that: after being treated by the method of the present invention, the B / C of the pyraclostrobin production wastewater after the above treatment is increased to 0.48, and the pH value of the wastewater is about 9.5; aerobic biochemical experiments are carried out after dilution, and biochemical COD degradation The rate is 75%.
Embodiment 3
[0057] A catalyst for alkaline hydrolysis of pyraclostrobin production wastewater, which is basically the same as in Example 1, the only difference being that in Example 3, the iron-based metal catalyst is FeCl 3 ·6H 2 O crystals.
[0058] The catalyst in Example 3 was used to treat pyraclostrobin production wastewater, and the treatment conditions were the same as in Example 1. The verification results of biochemical experiments show that: after being treated by the method of the present invention, the B / C of the pyraclostrobin production wastewater after the above treatment is increased to 0.45, and the pH value of the wastewater is about 9.5; aerobic biochemical experiments are carried out after dilution, and biochemical COD degradation The rate is 72%.
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