Monolayer, composite, gas separation material, filter, gas separation device and method for manufacturing composite
US-12128366-B2 · Oct 29, 2024 · US
US12465894B2 · US · B2
| Field | Value |
|---|---|
| Publication number | US-12465894-B2 |
| Application number | US-202519243768-A |
| Country | US |
| Kind code | B2 |
| Filing date | Jun 20, 2025 |
| Priority date | Dec 19, 2022 |
| Publication date | Nov 11, 2025 |
| Grant date | Nov 11, 2025 |
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A membrane including a polysulfone/polyethylene terephthalate (PSf/PET) support and an active layer on an outer surface of the PSf/PET support. The active layer comprises reacted units of a diacyl chloride compound, a tetra-amine compound, and a nanocomposite including graphitic carbon nitride and polypyrrole. The membrane of the present disclosure is self-cleaning following exposure to radiation and finds application in water decontamination and de-salination.
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The invention claimed is: 1 . A method for cleaning a fouled water purification membrane, comprising: irradiating the fouled water purification membrane with light having a wavelength of 400-700 nm to chemically degrade a pollutant present on the fouled water purification membrane and thereby form a photocatalytically active membrane; wherein the photocatalytically active membrane comprises a polysulfone/polyethylene terephthalate (PSf/PET) support; and an active layer on an outer surface of the PSf/PET support, wherein the active layer comprises reacted units of: a diacyl chloride compound; a tetra-amine compound; and a nanocomposite comprising a mixture of graphitic carbon nitride in the form of nanosheets and having triazine and heptazine rings and polypyrrole, wherein the photocatalytically active membrane has pores with an average diameter of less than 1 nm. 2 . The method of claim 1 , wherein the graphitic carbon nitride is bonded to at least one terminal end of the polypyrrole in the nanocomposite. 3 . The method of claim 1 , wherein the nanosheets have a thickness of 10-100 nm. 4 . The method of claim 1 , wherein the diacyl chloride compound is an aromatic ring substituted with two acyl chloride groups. 5 . The method of claim 1 , wherein the tetra-amine compound is a linear or branched aliphatic amine with of 2-50 carbons and four amine groups. 6 . The method of claim 1 , wherein the photocatalytically active membrane has 0.01 to 5 wt % of the nanocomposite based on the total weight of the active layer. 7 . The method of claim 1 , wherein particles of the active layer have a globular shape. 8 . The method of claim 1 , wherein particles of the active layer are not agglomerated. 9 . The method of claim 1 , wherein particles of the active layer have an average size of 50-200 nm. 10 . The method of claim 1 , wherein the photocatalytically active membrane comprises 50-70 at. % carbon, 25-35 at. % sulfur, 5-15 at. % oxygen, and 1-10 at. % nitrogen, based on a total number of atoms in the photocatalytically active membrane. 11 . The method of claim 1 , wherein the photocatalytically active membrane has a surface roughness of less than 24 nm. 12 . The method of claim 1 , wherein the photocatalytically active membrane has a water contact angle of less than 90°. 13 . The method of claim 1 , wherein the active photocatalytically active membrane covers at least 95% of the outer surface of the polysulfone/polyethylene terephthalate (PSf/PET) support. 14 . The method of claim 1 , wherein the photocatalytically active membrane has a permeate flux of 40 to 100 L m −2 h −1 at 10-30 bar. 15 . The method of claim 1 , wherein the photocatalytically active membrane rejects at least 60% of inorganic salts. 16 . The method of claim 1 , wherein the photocatalytically active membrane is self-cleaning following exposure to the light .
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