Method for treating highly concentrated resin-desorption liquid generated from wastewater deep purification

US9540268B2 · US · B2

Patent metadata
FieldValue
Publication numberUS-9540268-B2
Application numberUS-201113988512-A
CountryUS
Kind codeB2
Filing dateAug 12, 2011
Priority dateNov 24, 2010
Publication dateJan 10, 2017
Grant dateJan 10, 2017

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Abstract

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A method for treating highly concentrated resin-desorption liquid generated from wastewater deep purification, including channeling the highly concentrated desorption liquid generated from anion exchange resin treatment through a nanofiltration membrane, the liquid being separated into nanofiltration permeate that can be reused as the desorption agent and highly concentrated nanofiltration retentate; adding a coagulating agent to the highly concentrated nanofiltration retentate to generate coagulation-precipitation; subjecting the supernatant formed after the coagulation-precipitation process to Fenton oxidation or ozone oxidation; after the reaction, adding to the liquid an alkali solution for further coagulation-precipitation; then channeling the liquid so treated back to the biochemical system of biochemical effluent treatment for further biodegradation is provided. The recycled treatment of the highly concentrated desorption liquid consequently reduces the treatment cost and prevents secondary pollution by realizing innocuous treatment and reclamation of resin-desorption liquid as well as reduction of its total volume.

First claim

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What is claimed is: 1. A method for treating a highly concentrated resin-desorption liquid generated from a wastewater deep purification biochemical system, comprising: a) channeling the highly concentrated resin-desorption liquid generated from an anion exchange resin treatment of wastewater through a nanofiltration membrane and separating the highly concentrated resin-desorption liquid into a highly concentrated nanofiltration retentate and a nanofiltration permeate, wherein the nanofiltration permeate is reused as an desorption agent after oxidation; b) inducing a first coagulation-precipitation process by adding a coagulating agent to the highly concentrated nanofiltration retentate obtained in step a); c) subjecting a supernatant formed after the first coagulation-precipitation process to 1-5 hours of Fenton oxidation or ozone oxidation to obtain a solution; d) inducing a second coagulation-precipitation process by adding an alkali solution to the solution obtained in step c) for adjusting its pH value at 8.5-10.5; e) channeling a liquid obtained after the second coagulation-precipitation process of step d) to an activated sludge for further biodegradation; and f) channeling a liquid resulting from further biodegradation of the liquid obtained after the second coagulation-precipitation process of step d) with the activated sludge back to the wastewater deep purification biochemical system for further use in biodegradation, wherein the wastewater deep purification biochemical system uses an anion exchange resin. 2. A method for treating highly concentrated resin-desorption liquid generated from wastewater deep purification as defined in claim 1 , wherein the coagulating agent used in step b) is FeCl 3 .6H 2 O, FeSO 4 .7H 2 O, Al 2 (SO4) 3 .18H 2 O or polyaluminum chloride (PAC). 3. A method for treating highly concentrated resin-desorption liquid generated from wastewater deep purification as defined in claim 2 , wherein in step b) a mass percentage of the coagulating agent in the highly concentrated nanofiltration retentate is 1%-5%. 4. A method for treating highly concentrated resin-desorption liquid generated from wastewater deep purification as defined in claim 3 , wherein in step b) the pH value of the solution obtained after the first coagulation-precipitation process is 2-5. 5. A method for treating highly concentrated resin-desorption liquid generated from wastewater deep purification as defined in claim 1 , wherein in step c) is performed by Fenton oxidation, FeSO4-7H20 is used as an oxidant for Fenton oxidation, and a mass percentage of the FeSO4-7H20 in the solution is 0.1%-2%. 6. A method for treating highly concentrated resin-desorption liquid generated from wastewater deep purification as defined in claim 1 , wherein as to the Fenton reagent mentioned in step c), a mass percentage of 30% (by weight) H 2 O 2 solution in the solution is 1%-4%. 7. A method for treating highly concentrated resin-desorption liquid generated from wastewater deep purification as defined in claim 1 , wherein a concentration of the ozone used in step c) is 3 mg/L-10 mg/L. 8. A method for treating highly concentrated resin-desorption liquid generated from wastewater deep purification as defined in claim 1 , wherein the alkali solution used in step d) is NaOH or Ca(OH) 2 solution. 9. A method for treating highly concentrated resin-desorption liquid generated from wastewater deep purification as defined in claim 1 , wherein in step e), retention time in the activated sludge system is 12-18 h. 10. The method of treating highly concentrated resin-desorption liquid generated from wastewater deep purification as defined in claim 9 , further wherein, after 12 hours of treatment, the removal percentage of outflow chemical oxygen demand is 40%. 11. The method of treating highly concentrated resin-desorption liquid generated from wastewater deep purification as defined in claim 9 , further wherein, after 18 hours of treatment, the removal percentage of outflow chemical oxygen demand is 65%. 12. The method of treating highly concentrated resin-desorption liquid generated from wastewater deep purification as defined in claim 1 , further wherein, after 0.5 hours of precipitation in step d), the removal percentage of total organic carbon is 60%. 13. The method of treating highly concentrated resin-desorption liquid generated from wastewater deep purification as defined in claim 1 , further wherein, after 0.5 hours of precipitation in step d), the removal percentage of total organic carbon is 65%. 14. The method of treating highly concentrated resin-desorption liquid generated from wastewater deep purification as defined in claim 1 , further wherein, after 0.5 hours of precipitation in step d), the removal percentage of total organic carbon is 70%. 15. The method of treating highly concentrated resin-desorption liquid generated from wastewater deep purification as defined in claim 1 , further wherein, after 0.5 hours of precipitation in step d), the removal percentage of total organic carbon is 80%.

Assignees

Inventors

Classifications

  • by ion-exchange (ion-exchange in general B01J) · CPC title

  • Activated sludge processes · CPC title

  • C02F9/00Primary

    Multistage treatment of water, waste water or sewage · CPC title

  • Fenton's reagent · CPC title

  • using basic salts, e.g. of aluminium and iron · CPC title

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What does patent US9540268B2 cover?
A method for treating highly concentrated resin-desorption liquid generated from wastewater deep purification, including channeling the highly concentrated desorption liquid generated from anion exchange resin treatment through a nanofiltration membrane, the liquid being separated into nanofiltration permeate that can be reused as the desorption agent and highly concentrated nanofiltration rete…
Who is the assignee on this patent?
Li Aimin, Xu Ling, Fan Jun, and 3 more
What technology area does this patent fall under?
Primary CPC classification C02F9/00. Mapped technology areas include Chemistry & Metallurgy.
When was this patent published?
Publication date Tue Jan 10 2017 00:00:00 GMT+0000 (Coordinated Universal Time) (B2). Legal status and post-grant events are not shown on this page.
What related patents are in patentsdb?
We list 8 related publications on this page (citations in our corpus or others sharing the same primary CPC).