IP Library Granted Patent US 11,518,689
Granted Patent B2
US 11,518,689 · App. 16/869,471 · Granted Dec 6, 2022

Composition and method for capture and degradation of PFAS

Inventors: Radha K. Motkuri (Richland, WA); Sayandev Chatterjee (Richland, WA); Dushyant Barpaga (Richland, WA); Bernard P. McGrail (Pasco, WA)
Assignee: Battelle Memorial Institute
C02F1/288A62D3/115A62D3/38A62D3/40B01J20/226B01J27/188B01J27/19B01J27/195B01J27/198B01J31/24B01J35/004C02F1/283C02F1/30C02F1/32C02F1/583C02F1/725G01N27/07G01N27/226G01N27/48G01N33/1886A62D2101/22B01J2231/005B01J2531/74C02F1/281C02F1/285C02F2101/36C02F2103/06C02F2209/001C02F2209/003C02F2209/40C02F2303/16C02F2305/08C02F2305/10
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Quick Facts
Patent No.
US 11,518,689
App. No.
16/869,471
Granted
Dec 6, 2022
Kind
B2
Abstract

Materials for binding per- and polyfluoroalkyl substances (PFAS) are disclosed. A fluidic device comprising the materials for detection and quantification of PFAS in a sample is disclosed. The fluidic device may be configured for multiplexed analyses. Also disclosed are methods for sorbing and remediating PFAS in a sample. The sample may be groundwater containing, or suspected of containing, one or more PFAS.

Claims (31)

1. A method, comprising:

removing a per- or polyfluoroalkyl substance (PFAS) from a sample by

combining the sample with a composite sorbent, thereby sorbing the PFAS to the sorbent to form a PFAS-sorbent, the composite sorbent comprising at least two different materials selected from (a) a metal-organic framework (MOF), a covalent organic framework (COF), a covalent organic polymer (COP), zeolites, mesoporous silica, hierarchical porous carbon in combination with (b) at least one of a polymer, a zeolite, a covalent organic framework, mesoporous silica, a hierarchical porous carbon, a photocatalyst, a carbon nanotube, graphite, graphene, graphene oxide, a Prussian blue analog, or a metal oxide; and

separating the PFAS-sorbent from the sample, wherein

(i) the MOF, if present, does not comprise [Zr 6 O 4 (OH) 4 ] and 1,4-benzodicarboxylic acid (UiO-66), and/or

(ii) the polymer, if present, is not poly(ethylene-co-vinyl acetate).

2. The method of claim 1 , wherein combining the sample with the composite sorbent comprises flowing the sample through a bed of a column, the bed comprising the composite sorbent.

3. The method of claim 1 , wherein the sample has a contact time with the composite sorbent within a range of from 1 minute to 24 hours.

4. The method of claim 1 , further comprising heating the PFAS-sorbent to a temperature T 1 sufficient to thermally degrade the PFAS.

5. The method of claim 4 , wherein the PFAS-sorbent is heated to the temperature T 1 for a time period of from 1-24 hours.

6. The method of claim 4 , wherein the temperature T 1 is less than a temperature T 2 sufficient to thermally degrade the PFAS when not sorbed to the composite sorbent.

7. The method of claim 4 , wherein the temperature T 1 sufficient to thermally degrade the PFAS is within a range of from 50° C. to 200° C.

8. The method of claim 4 , further comprising heating the PFAS-sorbent in a solution comprising H 2 SO 4 , NaHSO 5 , Na 2 S 2 O 8 , FeSO 4 , H 2 O 2 , Na 2 S 2 O 4 , NaClO 3 , NaClO 4 , Na 2 S 2 O 5 , HCl, KI, NaNO 3 , HNO 3 , Fe( 0 ), Zn, Ni, Na 2 SO 3 , NaClO, Ca(OH) 2 , K 2 CrO 4 , Na 2 S 2 O 3 , Na 2 CO 3 , KMnO 4 , K 2 FeO 4 , NaBH 4 , NaOH, KOH, or any combination thereof.

9. The method of claim 1 , wherein the MOF comprises M 3 X(H 2 O) 2 O(BDC) 3 .nH 2 O where M is Cr or Fe, X is OH or F, BDC is 1,4-benzenedicarboxylate, and n is about 25.

10. The method of claim 1 , wherein the sample comprises groundwater, and the MOF comprises Fe 3 X(H 2 O) 2 O(BDC) 3 .nH 2 O where X is OH or F, BDC is 1,4-benzenedicarboxylate, and n is about 25.

11. The method of claim 1 , wherein the composite sorbent comprises a MOF and the MOF is redox-active.

12. The method of claim 1 , wherein the composite sorbent comprises a photocatalyst, the method further comprising exposing the PFAS-sorbent to light having a wavelength effective to excite the photocatalyst, thereby degrading the PFAS.

13. The method of claim 12 , wherein the photocatalyst comprises rhenium (II) dimethylphosphinoethane or a salt thereof.

14. The method of claim 12 , where the photocatalyst comprises a polyoxometalate.

15. The method of claim 14 , where the polyoxometalate comprises α-HP 3 M 12 O 40 .6 H 2 O, where M is W, Mo, V, Nb, Ta, or any combination thereof.

16. The method of claim 1 , wherein the PFAS comprises a PFAS of Table 1 or any combination thereof.

17. A method, comprising:

detecting presence of PFAS in a sample by

combining a sample with a sorbent comprising a redox-active metal-organic framework (MOF) to sorb PFAS present in the sample to the MOF to form a PFAS-sorbent;

measuring a redox signal of the combined sample and MOF using voltammetry; and

comparing the redox signal to a redox signal of the MOF in a sample that does not comprise a PFAS, wherein a difference between the redox signals indicates presence of PFAS in the sample.

18. The method of claim 17 , further comprising:

heating the PFAS-sorbent to a temperature T 1 sufficient to thermally degrade the PFAS.

19. The method of claim 17 , further comprising:

applying an oxidizing potential to the PFAS-sorbent, where the oxidizing potential is effective to oxidatively degrade the PFAS.

20. The method of claim 17 , wherein the PFAS comprises a PEAS of Table 1 or any combination thereof.

Assignments (2)
CONFIRMATORY LICENSE Recorded Jul 14, 2020
From: BATTELLE MEMORIAL INSTITUTE, PACIFIC NORTHWEST DIVISION
To: U.S. DEPARTMENT OF ENERGY
Reel/Frame 053206/0059 →
ASSIGNMENT OF ASSIGNOR'S INTEREST Recorded May 8, 2020
From: MOTKURI, RADHA K.; CHATTERJEE, SAYANDEV; BARPAGA, DUSHYANT; MCGRAIL, BERNARD P.
To: BATTELLE MEMORIAL INSTITUTE
Reel/Frame 052609/0420 →
Continuity (4)
Provisional Application 62980681 · Feb 24, 2020
Provisional Application 62942637 · Dec 2, 2019
Provisional Application 62851854 · May 23, 2019
Related Publication 20200369536A1 · Nov 26, 2020
Cited By (9)
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