Particulate crystalline nanocomposite and adsorbent

US12486180B1 · US · B1

Patent metadata
FieldValue
Publication numberUS-12486180-B1
Application numberUS-202519250482-A
CountryUS
Kind codeB1
Filing dateJun 26, 2025
Priority dateJun 26, 2025
Publication dateDec 2, 2025
Grant dateDec 2, 2025

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  5. First independent claim

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Abstract

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A method of immobilizing contaminants disposed in an aqueous medium, the method including contacting the aqueous medium with a CaHPO 4 /Ca 6 Si 6 O 17 (OH) 2 /g-C 3 N 4 particulate crystalline nanocomposite for a sufficient contact time to permit adsorption of the contaminants. The particulate crystalline nanocomposite includes: a calcium hydrogen phosphate (CaHPO 4 ) crystalline phase; a calcium silicate hydroxide (Ca 6 Si 6 O 17 (OH) 2 ) crystalline phase; a silicon dioxide (SiO 2 ) crystalline phase; and, a graphitic carbon nitride (g-C 3 N 4 ) crystalline phase, wherein at least a fraction of the g-C 3 N 4 is in the form of mesoporous nanosheets.

First claim

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The invention claimed is: 1 . A method of immobilizing contaminants disposed in an aqueous medium, the method comprising contacting the aqueous medium with a particulate crystalline nanocomposite for a sufficient contact time to permit adsorption of the contaminants, the particulate crystalline nanocomposite comprising: a calcium hydrogen phosphate (CaHPO 4 ) crystalline phase; a calcium silicate hydroxide (Ca 6 Si 6 O 17 (OH) 2 ) crystalline phase; a silicon dioxide (SiO 2 ) crystalline phase; and, a graphitic carbon nitride (g-C 3 N 4 ) crystalline phase, wherein at least a fraction of the graphitic-C 3 N 4 is in the form of mesoporous nanosheets. 2 . The method according to claim 1 , wherein the contaminants comprise organic contaminants selected from the group consisting of: a polyaromatic hydrocarbon, a halogenated polyaromatic hydrocarbon; a phenol, a halogenated phenol; a furan, a halogenated furan; a dioxine, a halogenated dioxine; a biphenyl, a halogenated phenyl; and, an organic dye. 3 . The method according to claim 1 , wherein the contaminants comprise inorganic contaminants selected from the group consisting of: a radioactive nuclide; a heavy metal; and, a metalloid. 4 . The method according to claim 1 , wherein based on the weight of the particulate crystalline nanocomposite: CaHPO 4 is present in an total amount of from about 20 to about 40 weight percent (wt. %); Ca 6 Si 6 O 17 (OH) 2 is present in an amount of about 20 to about 30 wt. %; SiO 2 is present in an amount of from about 1 to about 10 wt. %; and, g-C 3 N 4 is present in an amount of about 20 to about 30 wt. %. 5 . The method according to claim 1 , wherein the particulate crystalline nanocomposite comprises acicular particles of Ca 6 Si 6 O 17 (OH) 2 having a median length of from about 20 to about 80 nanometers (nm), as determined by Transmission Electron Microscopy. 6 . The method according to claim 1 , wherein the particulate crystalline nanocomposite comprises aggregates of the mesoporous nanosheets of g-C 3 N 4 with substantially spherical particles of SiO 2 and CaHPO 4 . 7 . The method according to claim 1 , wherein the particulate crystalline nanocomposite comprises aggregates of: the mesoporous nanosheets of g-C 3 N 4 ; and, substantially spherical particles of SiO 2 and CaHPO 4 having a median particle size of from about 5 to about 30 nm, as determined by Transmission Electron Microscopy. 8 . The method according to claim 1 , wherein at least about 50 wt. % of the g-C 3 N 4 is in the form of mesoporous nanosheets. 9 . The method according to claim 1 , wherein at least about 80 wt. % of the g-C 3 N 4 is in the form of mesoporous nanosheets. 10 . The method according to claim 1 , wherein the particulate crystalline nanocomposite has an average pore diameter of from about 10 to about 25 nm, as determined by Barrett-Joyner-Halenda (BJH) desorption analysis. 11 . The method according to claim 1 , wherein the particulate crystalline nanocomposite has an average pore diameter of from about 15 to about 25 nm, as determined by BJH desorption analysis. 12 . The method according to claim 1 , wherein the particulate crystalline nanocomposite has a pore volume of from about 0.1 to about 0.4 cm 3 /g, as determined by BJH desorption analysis. 13 . The method according to claim 1 , wherein the particulate crystalline nanocomposite has a pore volume of from about 0.2 to about 0.3 cm 3 /g, as determined by BJH desorption analysis. 14 . The method according to claim 1 , wherein the particulate crystalline nanocomposite has a hysteresis loop of Type H3 (IUPAC Classification), as determined by nitrogen (N 2 ) adsorption-desorption analysis at 77 kelvin (K). 15 . The method according to claim 1 further comprising preparing the particulate crystalline nanocomposite by: forming a solution of a calcium salt and an alkali metal silicate in a solvent comprising water and a C 1 -C 4 alkanol; heating the solution at a temperature of from about 150 to about 250 degrees Celsius (° C.) to form a dry product of CaSiO 3 ; forming g-C 3 N 4 by heating urea in a closed vessel at a temperature of from about 500 to about 700° C.; dispersing the CaSiO 3 , graphitic-C 3 N 4 , and P 2 O 5 in a polar protic solvent and heating the dispersion at a temperature of from about 150 to about 250° C. at a pressure of from about 2 to about 8 Bar; and, separating the particulate crystalline nanocomposite from the heated dispersion. 16 . The method according to claim 1 , wherein the contact time of the aqueous medium with the particulate crystalline nanocomposite is from about 1 to about 120 minutes (min). 17 . The method according to claim 1 , wherein the contact time of the aqueous medium with the particulate crystalline nanocomposite is from about 5 to about 30 min. 18 . The method according to claim 1 , wherein a fixed volume of the aqueous medium is provided in which the particulate crystalline nanocomposite is dispersed. 19 . The method according to claim 1 , wherein a flow of the aqueous medium contacts a membrane in which the particulate crystalline nanocomposite is disposed. 20 . The method according to claim 1 , wherein the particulate crystalline nanocomposite is provided in an amount of from about 0.1 to about 5 grams per liter (g/L) of the aqueous medium.

Assignees

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Classifications

  • with size in the range 1-100 nanometers, e.g. nanosized particles, nanofibers, nanotubes, nanowires or the like (carbon nanostructures B01J20/205) · CPC title

  • Radioactive compounds · CPC title

  • Wastewater from hospitals, laboratories and the like, heavily contaminated by pathogenic microorganisms · CPC title

  • Heavy metals or heavy metal compounds · CPC title

  • Nanoparticles or nanotubes · CPC title

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What does patent US12486180B1 cover?
A method of immobilizing contaminants disposed in an aqueous medium, the method including contacting the aqueous medium with a CaHPO 4 /Ca 6 Si 6 O 17 (OH) 2 /g-C 3 N 4 particulate crystalline nanocomposite for a sufficient contact time to permit adsorption of the contaminants. The particulate crystalline nanocomposite includes: a calcium hydrogen phosphate (CaHPO 4 ) crystalline phase; a calc…
Who is the assignee on this patent?
Imam Mohammad Ibn Saud Islamic Univ
What technology area does this patent fall under?
Primary CPC classification C02F1/281. Mapped technology areas include Chemistry & Metallurgy.
When was this patent published?
Publication date Tue Dec 02 2025 00:00:00 GMT+0000 (Coordinated Universal Time) (B1). Legal status and post-grant events are not shown on this page.
What related patents are in patentsdb?
We list 1 related publication on this page (citations in our corpus or others sharing the same primary CPC).