Composite LED Module and Water Quality Monitoring Device Using the Same
US-2020209208-A1 · Jul 2, 2020 · US
US12510470B2 · US · B2
| Field | Value |
|---|---|
| Publication number | US-12510470-B2 |
| Application number | US-202218569282-A |
| Country | US |
| Kind code | B2 |
| Filing date | Jun 8, 2022 |
| Priority date | Jun 13, 2021 |
| Publication date | Dec 30, 2025 |
| Grant date | Dec 30, 2025 |
A practical reading order for non-experts. Skip the full description unless you need deep technical detail.
What the patent document calls the invention.
A short plain-language summary of the technical disclosure.
Who owns or filed the patent and who is credited as inventor.
Filing, priority, publication, and grant dates set the timeline.
The legal scope of protection — read this for what is actually claimed.
Technology tags used to group this patent with similar filings.
Prior art links and similar publications in this corpus.
Official abstract text for this publication.
A method for real-time determining a concentration level of nitrate in a water sample collected from soil at a given site, the water sample contains an unknown composition and unknown concentration of DOC, the method includes: (A) during an offline stage: (a.1) obtaining a testing sample from the soil; (a.2) determining first and second wavelengths correlated, respectively, to concentration levels of the DOC and nitrate in the testing sample; (a.3) creating a calibration equation for this site; and, (B) during real-time: (b.1) separately impinging on a real-time water sample from the soil light in said two wavelengths; (b.2) determining respective absorbances by the real-time sample in said two wavelengths; and (c) substituting the respective absorbances in the calibration equation to obtain the nitrate concentration in the real-time sample.
Opening claim text (preview).
The invention claimed is: 1 . A method for determining a concentration of nitrate in a water sample collected from soil at a given site, said water sample also contains an unknown composition and unknown concentration of Dissolved Organic Carbon (DOC), the method comprising: a. during an offline stage: collecting a testing sample from the site; analyzing the testing sample to determine a first wavelength in which a light absorbance by the testing sample is correlated to the concentration level of the DOC in the testing sample; further analyzing the testing sample to determine a second wavelength in which a light absorbance by the testing sample is correlated to the concentration level of the nitrate in the testing sample; based on the above two-step offline analysis, creating a multivariate polynomial calibration equation for use during a real-time stage analysis; and b. during a real-time stage analysis: collecting a real-time water sample from the site's soil; impinging on the real-time sample light in said first wavelength, measuring the real-time sample's absorbance, and recording the measured absorbance as a first absorbance value; impinging on the real-time sample light in said second wavelength, measuring the real-time sample's absorbance, and recording the measured absorbance as a second absorbance value; and substituting in said calibration equation the first absorbance value and the second absorbance value, or values relative thereon, and calculating to determine the nitrate concentration in the real-time sample. 2 . The method of claim 1 , wherein said offline stage comprises a creation a calibration matrix of samples from the from the testing sample, and wherein said analyses steps are performed on the calibration matrix. 3 . The method of claim 2 , wherein said first wavelength and said second wavelength are determined by: dividing the calibration matrix of samples to a plurality of sub-samples, and dividing the plurality of sub-samples to two groups; differently enriching in a controlled manner the sub-samples in said first group by nitrate; differently diluting in a controlled manner the sub-samples in said second group by DDW; dividing a wide light spectrum into a plurality of wavelengths to form a plurality of discrete wavelengths; in each discrete wavelength, impinging light on each sub-sample within said two groups, and recording respectively the absorbance by the sub-sample; and analyzing said respective absorbances to determine said first wavelength and said second wavelength. 4 . The method of claim 3 , wherein the creation of the calibration equation is based on applying a multivariate regression technique on the variety of recorded absorbances. 5 . The method of claim 1 , wherein at least one of said correlations is a linear or higher order correlation. 6 . The method of claim 1 , wherein the offline stage is performed separately for each site, to determine a calibration equation that is specific to each site. 7 . The method of claim 1 , for further determining the concertation of DOC in the sample. 8 . The method of claim 1 , wherein said correlations define spectrum regions, respectively, in which the extent of correlation R 2 is higher than 0.8. 9 . The method of claim 1 , wherein said correlations define spectrum regions, respectively, in which the extent of correlation R 2 is higher than 0.85, 0.9, 0.95, or 0.98 in either or both said concentration levels determinations. 10 . A system for determining in real-time a concentration of nitrate in a water sample collected from soil at a given site, said water sample also contains an unknown composition and unknown concentration of Dissolved Organic Carbon (DOC), the system comprising: a first light source operating at a predetermined first wavelength in which light absorbance by the sample is correlated to a concentration level of DOC in the sample; a second light source operating at a second wavelength in which light absorbance by the sample is correlated to a concentration level of nitrate in the sample; at least partially transparent cell for containing said water sample, wherein each said light sources is directed to impinge light on said cell containing the sample; and an analysis unit receiving a first sample absorbance in said first wavelength, and a second sample absorbance in said second wavelength, and calculating the concentration of nitrate in the sample based on said two absorbances, and a predetermined calibration equation; wherein said correlations define spectrum regions, respectively, in which the extent of correlation R 2 is higher than 0.8. 11 . The system of claim 10 , wherein at least one of said correlations is a linear or higher order correlation. 12 . The system of claim 10 , wherein at least one of said light sources are of LED or UV lamp. 13 . The system of claim 10 , wherein said predetermined calibration equation is specifically determined for each given site. 14 . The system of claim 10 , for further determining the concentration of the DOC in the water sample. 15 . The system of claim 10 , wherein said correlations define spectrum regions, respectively, in which the extent of correlation R 2 is higher than 0.8. 16 . The system of claim 10 , wherein said correlations define spectrum regions, respectively, in which the extent of correlation R 2 is higher than 0.85, 0.9, 0.95, or 0.98 in either or both said concentration levels determinations.
Calibration; base line adjustment; drift compensation · CPC title
Water · CPC title
Determining the state of nitrification · CPC title
using ultraviolet light (G01N21/39 takes precedence) · CPC title
Using chemometrical methods · CPC title
Related publications grouped by family.
Answers are generated from the same data shown on this page.