Method for treating pesticide residue and heavy metal mercy in sewage
A sewage and pretreatment technology, which is applied in the direction of chemical instruments and methods, filtration treatment, sedimentation treatment, etc., can solve the problems of secondary pollution of soil and water sources, etc., and achieve the effect of improving treatment effect, good application prospect and high removal efficiency
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Embodiment 1
[0025] The treatment of embodiment 1 mercury and pesticide residual sewage
[0026] When the sewage enters the water, the concentration of mercury is 30mg / L, dimethoate 20mg / L, fenitrothion 20mg / L, methomyl 20mg / L.
[0027] Pretreatment: remove the suspended solids in the treated sewage by filtration and sedimentation;
[0028] Main treatment: Add the bacteria Pseudomonas putida SPl CGMCC N0.3887 (from CN 102373161A) cultivated to the logarithmic growth phase to the sewage, and flow culture for 24 hours at room temperature to remove the sewage HG;
[0029] Post-treatment: the sewage is treated overnight through the zeolite and activated carbon adsorption pool again to adsorb pesticide residues;
[0030] After the treated sewage is disinfected, it is directly discharged or reused. After testing, the concentration of mercury was 2.2mg / L, dimethoate 15.3mg / L, fenitrothion 14.4mg / L, methomyl 16.5mg / L.
Embodiment 2
[0031] Example 2 Transformation and acquisition of degradable pesticide genes
[0032] According to the method disclosed in CN1970741A, CYP9G2 and POR genes were cloned. The following modifications were made to the CYP9G2 gene. On the basis of GenBank: AB096739, the corresponding Ser30Ile (indicating that the Ser at position 30 was mutated to Ile), Phe56Gly, Gly77Lys, Phe186Ala, Leu276Ile, Leu311Asp, Val366Gly, Val409Cys, Asp415Pro, Trp426Leu, Lys476Gly, Leu500Ala, and the mutation sites were respectively introduced into the protein shown in GenBank: AB096739, thereby constructing different mutant CYP9G2 genes (can be obtained by referring to the preparation method of the prior art). The mutated CYP9G2 gene and the POR gene were respectively connected to the expression vector according to the method for preparing CN1970741A, and the successfully verified recombinant plasmid was transformed into the Pseudomonas putida SP1 CGMCC No. 3887 strain, which was successfully constructe...
Embodiment 3
[0033] Example 3 Verification of sewage degradation effect
[0034] The strains containing different mutant proteins were respectively followed the method of Example 1 to verify the treatment effect on sewage. When the sewage enters the water, the concentration of mercury is 30mg / L, dimethoate 20mg / L, fenitrothion 20mg / L, methomyl 20mg / L. The strains and bacteria transformed with unmutated CYP9G2 and POR genes were used as controls. The specific results are as follows:
[0035] strain Mercury concentration (mg / L) Dimethoate (mg / L) Fenitrothion (mg / L) Methomyl (mg / L) Ser30Ile strain (SC1 strain) 0.1 0.4 0.6 0.6 Phe56Gly strain (SC2 strain) 0.2 0.5 0.5 0.7 Gly77Lys strain (SC3 strain) 0.1 0.4 0.4 0.8 Phe186Ala strain (SC4 strain) 0.2 0.6 0.3 0.7 Leu276Ile strain (SC5 strain) 0.2 0.5 0.5 0.8 Leu311Asp strain (SC6 strain) 0.3 0.4 0.4 0.6 Val366Gly strain (SC7 strain) 0.1 0.3 0.3 0.5 Val409Cys str...
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