Co-used iron-carbon micro-electrolysis and photo degradation two-section perfluoro octanoic acid degradation method
An iron-carbon micro-electrolysis, perfluorooctanoic acid technology, applied in chemical instruments and methods, water/sewage multi-stage treatment, water pollutants, etc., can solve the problems of few applications, low degradation efficiency, slow speed, etc. simple conditional effect
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Embodiment 1
[0030] An iron-carbon micro-electrolysis-VUV / Fenton two-stage method for synergistically degrading perfluorooctanoic acid in water (iron-carbon micro-electrolysis), the method is composed of iron-carbon micro-electrolysis reaction and photodegradation reaction. The iron-carbon micro-electrolysis reaction device includes a stirring paddle 1 and a reactor 3 containing an aqueous solution containing perfluorooctanoic acid, and the stirring paddle 1 is placed in the middle of the reactor 3 . The reactor 3 is a cylindrical vessel made of polytetrafluoroethylene, on which a sampling tube 2 is arranged, and the aqueous solution 4 in the reactor 3 is composed of a perfluorooctanoic acid aqueous solution, activated carbon and iron powder. The photodegradation reaction device includes a timing constant temperature magnetic stirrer 10 and a photodegradation reactor 9, and the photodegradation reactor 9 is placed on the timing constant temperature magnetic stirrer 10. An ultraviolet lamp ...
Embodiment 2
[0040] The difference between this embodiment and embodiment 1 is:
[0041] Present embodiment does not carry out iron-carbon micro-electrolysis reaction, comprises the following steps:
[0042] a) Join the PFOA solution to be treated in the photodegradation reactor, turn on the magnetic stirrer, close the compartment 11, turn on the ultraviolet lamp 7 (the exterior is provided with an ultraviolet lamp lampshade 8), and react for 6 hours:
[0043] b) Turn off the UV lamp power supply 6, the reaction is finished, and the water is discharged, and the fluoride ion selective electrode is used to measure F - concentration to determine the defluorination rate.
[0044] After testing, the UV lamp alone has a defluorination rate of 39.89% for PFOA, indicating that the UV lamp has a certain photolysis effect on PFOA.
Embodiment 3
[0046] The difference between this embodiment and embodiment 1 is:
[0047] The method for utilizing the device to degrade PFOA in water comprises the steps:
[0048] a) Carry out pretreatment to activated carbon, take quantitative activated carbon, soak in the solution to be treated for 24 hours, rinse with ultrapure water, and dry for subsequent use;
[0049]b) Add the PFOA solution to be treated into the reactor, add pretreated activated carbon 12.5g / L and iron powder 7.5g / L at the same time, adjust the pH of the reaction solution to 3.0 with 0.1mol / L NaOH and HCl; open stirring paddle, react for 1 hour;
[0050] c) Turn off the stirring paddle, the iron-carbon micro-electrolysis reaction is completed, filter the water, inject it into the photodegradation reactor, adjust the pH to 3.0 with 0.1mol / L NaOH and HCl, turn on the ultraviolet power supply, and react for 6 hours;
[0051] d) Turn off the ultraviolet light power supply, the reaction is completed, and the water is ...
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Abstract
Description
Claims
Application Information
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