Advanced non-toxic radiation shielding materials from tailored brine sludge and a process for the preparation thereof
US-2017257987-A1 · Sep 7, 2017 · US
US9890081B2 · US · B2
| Field | Value |
|---|---|
| Publication number | US-9890081-B2 |
| Application number | US-201615245521-A |
| Country | US |
| Kind code | B2 |
| Filing date | Aug 24, 2016 |
| Priority date | Sep 2, 2015 |
| Publication date | Feb 13, 2018 |
| Grant date | Feb 13, 2018 |
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Brine sludge is an industrial waste generated in chloral alkali industry. The generated brine sludge waste is dumped into landfills and contains barium sulphate, calcium carbonate, magnesium hydroxide, sodium chloride, clay, and toxic elements like chromium, zinc, copper, and vanadium, therefore posing an environmental threat. Consequently, there is an urgent need to convert toxic brine sludge waste into its non-toxic form. The present invention thus aims to achieve total utilization of this brine sludge for making functionalized brine sludge material useful for a broad application spectrum.
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We claim: 1. A functionalized brine sludge material comprising: 10 g to 50 g of brine sludge; 50 g to 100 g of fly ash; 6 g to 13 g of sodium hydroxide; 250 ml to 500 ml of ethylene glycol; 1 g to 10 g of cetyl trimethyl ammonium bromide; and 12 ml to 26 ml of water. 2. The material as claimed in claim 1 , wherein the material is useful for the preparation of radiation shielding materials, geopolymeric materials, and chemically designed composite materials. 3. The material as claimed in claim 1 , wherein the material comprises 45 g of brine sludge, 45 g of fly ash, 6 g of sodium hydroxide, 300 ml of ethylene glycol, 10 g of cetyl trimethyl ammonium bromide, and 12 ml of water. 4. A process for the preparation of the functionalized brine sludge material as claimed in claim 1 , the process comprising: (a) refluxing a homogenized mixture of brine sludge, fly ash, sodium hydroxide, ethylene glycol, cetyl trimethyl ammonium bromide, and water in a round bottom flask; and (b) filtering the mixture as obtained in step (a) followed by drying in an air oven at a temperature of 100 to 110 degrees C. for a period of 1 to 2 hours, resulting in an in-situ synthesized functionalized brine sludge material. 5. The process as claimed in claim 4 , wherein refluxing in step (a) is done at a temperature of 190 to 250 degrees C. for a duration of 2 to 6 hours using conventional heating. 6. The process as claimed in claim 4 , wherein refluxing in step (a) is done at a temperature of 40 to 45 degrees C. for a duration of 15 to 20 minutes using microwave heating. 7. The process as claimed in claim 4 , wherein drying in step (b) is done at a temperature of 110 degrees C. for a duration of 1 to 2 hours.
Microwaves · CPC title
Ash cements, e.g. fly ash cements (fly ash as filler C04B18/08); Cements based on incineration residues, e.g. alkali-activated slags from waste incineration (alkali-activated combustion residues as such C04B7/243; mixtures of the lime-pozzuolane type C04B28/18); Kiln dust cements · CPC title
Halogen-containing compounds · CPC title
Use of waste materials as fillers for mortars or concrete · CPC title
Wet materials, e.g. slurries · CPC title
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