CN105044042A - Concentration detection method of manganese in trace amount in drinking water and waveguide used therein - Google Patents
Concentration detection method of manganese in trace amount in drinking water and waveguide used therein Download PDFInfo
- Publication number
- CN105044042A CN105044042A CN201510235554.4A CN201510235554A CN105044042A CN 105044042 A CN105044042 A CN 105044042A CN 201510235554 A CN201510235554 A CN 201510235554A CN 105044042 A CN105044042 A CN 105044042A
- Authority
- CN
- China
- Prior art keywords
- manganese
- glass
- waveguide
- sample
- metal film
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Abstract
The invention relates to a concentration detection method of manganese in trace amount in drinking water and a waveguide used therein. The concentration detection method includes the following steps: 1) with a strong oxidant, oxidizing manganese ions in the drinking water to form MnO4<-> ion to obtain a sample for later use; 2) through a peristaltic pump, outputting the sample into a sample chamber of the waveguide; and 3) irradiating the surface of the waveguide by laser, receiving a reflected light through CCD and detecting the gray level of the center of a black line through the CCD and calculating the concentration of manganese in trace amount. The waveguide is formed by assembling flat sheet glass, a glass gasket and a glass substrate from top to bottom, wherein an upper metal film layer is deposited on the upper surface of the flat sheet glass and a lower metal film layer is deposited on the upper surface of the glass substrate. The glass gasket is provided with a sample inlet and a sample outlet, and the space in the glass gasket is the sample chamber.
Description
Technical field
The present invention relates to and a kind ofly drink Trace Manganese in Water concentration detection method and the waveguide for the method.
Background technology
Manganese is one of necessary trace element of human body and animals and plants, but the manganese of excess intake then can produce ill-effect to body.Manganese enters human body by water and food, in organ-tissue enrichments such as liver, kidney, brains, and produces infringement in various degree to the breathing of people, nerve and reproductive system.
Therefore, to the detection of Fe content in water, for ensureing that health has great importance.
In current detection water, the common method of Fe content has following several: atomic absorption method, the mensuration of manganese in water can be directly used in, because the method has the features such as anti-interference, sensitivity is higher, accuracy is good, widespread use in the industries such as environmental protection, edge gold medicine, but it measures process technology and requires higher, instrument needs the atomising device of the sample solution of manganese, and testing cost is higher.By Formaldehyde Oxime Method application is comparatively wide, in the world one of analytical approach becoming standard.But By Formaldehyde Oxime Method reagent used is not easy to preserve.Potassium metaperiodate oxidizing process selectivity is better, be often used, but sensitivity is lower, cannot be used in the detection of drinking Trace Manganese in Water concentration.
Summary of the invention
Goal of the invention of the present invention is that providing a kind of drinks Trace Manganese in Water concentration detection method and the waveguide for the method, and to drinking, Trace Manganese in Water Concentration Testing is effective, and testing cost is low, easy to operate.
The present invention is based on same inventive concept, there are two independent technique schemes:
1, one drinks Trace Manganese in Water concentration detection method, it is characterized in that:
Utilize strong oxidizer that the manganese ion in potable water is oxidized to mauve ion
ion, for subsequent use as sample;
Utilize peristaltic pump by the sample chamber of above-mentioned sample output waveguide;
Irradiate the surface of waveguide with laser, receive reflected light with CCD, by the gray scale of CCD detection black line center, calculate and obtain Trace Amount Manganese concentration.
Irradiate the surface of waveguide with the laser that wavelength is 532nm, the angle of divergence of laser is less than 0.3mrad.
Utilize strong oxidizer that the manganese ion in potable water is oxidized to mauve ion
during ion, the reducing substances in potable water and chlorion need be removed, utilize H
3pO
4the red Fe sheltered in potable water
3+.
Strong oxidizer is potassium metaperiodate or ammonium persulfate.
2, an above-mentioned waveguide of drinking Trace Manganese in Water concentration detection method, is characterized in that: sheet glass, glass seal, glass substrate from top to bottom fit together; The upper surface of sheet glass deposits upper strata metal film, and the upper surface of glass substrate deposits lower metal film; Glass seal has sample inlet and sample export, and the space in glass seal is sample chamber.
The material of upper strata metal film is silver, and the thickness of upper strata metal film is 35nm.
The material of sheet glass is optical glass, and its thickness is 300 μm.
The material of glass seal is optical glass, and its thickness is about 500 μm.
The material of lower metal film is silver, and its thickness is about 200nm.
The material of glass substrate is optical glass, and its thickness is 1000 μm.
The beneficial effect that the present invention has:
The present invention utilizes strong oxidizer to be oxidized to mauve by the manganese ion in potable water
ion, as sample, utilizes peristaltic pump by the sample chamber of above-mentioned sample output waveguide; Irradiate the surface of waveguide with laser, receive reflected light with CCD, by the gray scale of CCD detection black line center, calculate and obtain Trace Amount Manganese concentration.The present invention's wavelength is the surface of the laser irradiation waveguide of 532nm, due to exciting of ultrahigh-order mode, will occur the absorption black line occurred because of attenuated total reflection (ATR) in reflected light.Due to the minimal value R of ATR absorption peak
minclosely related with the extinction coefficient κ of sample, and the size of κ is proportional to the concentration of sample, therefore, by the gray scale (R of CCD detection black line center
min), can be calculated Trace Amount Manganese concentration.The present invention's waveguide, as sample chamber and resonant cavity, has high power density and high-quality-factor (Q value), and detect and have high sensitivity, Detection results is good, and apparatus structure is simple, testing cost is low, be easy to carry, easy to operate, just with popularization.
Waveguide of the present invention is from top to bottom fitted together by sheet glass, glass seal, glass substrate; The upper surface of sheet glass deposits upper strata metal film, and the upper surface of glass substrate deposits lower metal film; Glass seal has sample inlet and sample export, and the space in glass seal is sample chamber.The material of upper strata metal film is silver, and the thickness of upper strata metal film is 35nm.The material of sheet glass is optical glass, and its thickness is 300 μm.The material of glass seal is optical glass, and its thickness is about 500 μm.The material of lower metal film is silver, and its thickness is about 200nm.The material of glass substrate is optical glass, and its thickness is 1000 μm.The design of waveguiding structure of the present invention, the selection of parameter, can ensure to have best Detection results.
Accompanying drawing explanation
Fig. 1 is the assembling schematic diagram of waveguide of the present invention;
Fig. 2 is that Trace Manganese in Water concentration C CD detects schematic diagram.
Embodiment
As shown in Figure 1, sheet glass 1, glass seal 2, glass substrate 3 from top to bottom fit together; The upper surface of sheet glass 1 deposits upper strata metal film, and the upper surface of glass substrate 3 deposits lower metal film 4; Glass seal 2 has sample inlet 5 and sample export 6, and the space in glass seal 2 is sample chamber.The material of upper strata metal film is silver, and the thickness of upper strata metal film is 35nm.The material of sheet glass 1 is optical glass, and its thickness is 300 μm.The material of glass seal 2 is optical glass, and its thickness is about 500 μm.The material of lower metal film 4 is silver, and its thickness is about 200nm.The material of glass substrate 3 is optical glass, and its thickness is 1000 μm.
During detection, first, the cuvette in colour developing box is utilized to add the potable water closing manganese, in phosphoric acid solution (concentration is 2.3mol/L), add potassium metaperiodate and sensitive chromogenic reaction occurs manganese, generate aubergine permanganate, be oxidized to mauve by the manganese ion in potable water
ion, for subsequent use as sample; In process color, reducing substances and chlorion can disturb colour developing, must remove in advance, Fe
3+solution can be made to be yellow, to utilize H
3pO
4the red Fe sheltered in potable water
3+.
Utilize peristaltic pump by the sample chamber of above-mentioned sample output waveguide;
Irradiate the surface of waveguide with the laser that wavelength is 532nm, the angle of divergence of laser is less than 0.3mrad.Reflected light is received by CCD detection element, because laser has live width and the angle of divergence of nanometer scale, by designing in advance, can guarantee to excite a ultrahigh-order mode near incident angle, due to exciting of ultrahigh-order mode, the absorption black line occurred because of attenuated total reflection (ATR) in reflected light, will be there is.
The minimal value R of ATR absorption peak
minprovided by following formula:
Wherein, Im (β °) represents intrinsic loss, and the extinction coefficient κ of intrinsic loss and sample is closely related, Im (Δ β
l) represent radiation loss.β °=k
0n
0sin θ is guided mode propagation constant, and k
0=2 π/λ are the propagation constant in air, n
0for air refraction, θ is incident angle.When intrinsic loss equals radiation loss Im (β °)=Im (Δ β
l) time, there is R
min=0.R
min=0 is also the starting condition (sample is aqueous solution, and the concentration of manganese is zero) of testing.When in solution, the concentration of manganese increases, the size due to extinction coefficient κ is proportional to the concentration of sample, causes the increase of intrinsic loss Im (β °), thus makes R
minbecome large.Therefore, by the gray scale R of CCD detection black line center
min, can be calculated Trace Amount Manganese concentration, R
minthe scale of change is determined by the measurement of standard solution.
Suppose the wavelength X=532nm of incident laser, the dielectric coefficient ε of upper strata metal film
1=-10.5+i0.8, thickness h
1=35nm, the refractive index n of sheet glass
2=1.50, thickness is h
2=300 μm, the thickness h of glass seal and sample chamber
4=h
3=500 μm, the dielectric coefficient ε of lower metal film
5=ε
1=-10.5+i0.8, thickness h
5=200nm.The refractive index n of initial sample
3=1.3342, do not conforming in manganese situation, the imaginary part of sample refractive index is 0, is water white liquid.If laser is decided to be θ at the center incident angle of waveguide surface
in=4.56 °, then by the attenuated total reflection that can be calculated as shown in Figure 2 (ATR) curve, the reflectivity R of ATR peak base
min≈ 0.If experiment, then manifest the maximum black line of a gray scale in reflected light.Along with the increase of manganese concentration, due to the effect with developer, color from light to dark, shows that the imaginary part (extinction coefficient κ) of sample refractive index becomes large gradually by 0, the gray scale of the black line that CCD detection arrives also (R from large to small
minchange from small to big).If the reflectivity change using 1% as the resolution of ccd detector, then may detect extinction coefficient changes delta κ=10
-6.In the detection of reality, realize the detection resolution of 0.1 μ g/L.
Claims (10)
1. drink a Trace Manganese in Water concentration detection method, it is characterized in that:
Strong oxidizer is utilized to be oxidized to mauve by the manganese ion in potable water
ion, for subsequent use as sample;
Utilize peristaltic pump by the sample chamber of above-mentioned sample output waveguide;
Irradiate the surface of waveguide with laser, receive reflected light with CCD, by the gray scale of CCD detection black line center, calculate and obtain Trace Amount Manganese concentration.
2. according to claim 1ly drink Trace Manganese in Water concentration detection method, it is characterized in that: the surface irradiating waveguide with the laser that wavelength is 532nm, the angle of divergence of laser is less than 0.3mrad.
3. according to claim 2ly drink Trace Manganese in Water concentration detection method, it is characterized in that: utilize strong oxidizer that the manganese ion in potable water is oxidized to mauve ion
during ion, the reducing substances in potable water and chlorion need be removed, utilize H
3Po
4the red Fe sheltered in potable water
3+.
4. drink Trace Manganese in Water concentration detection method according to claim 1-3 described in any one, it is characterized in that: strong oxidizer is potassium metaperiodate or ammonium persulfate.
5. for a waveguide for method described in claim 1, it is characterized in that: sheet glass, glass seal, glass substrate from top to bottom fit together; The upper surface of sheet glass deposits upper strata metal film, and the upper surface of glass substrate deposits lower metal film; Glass seal has sample inlet and sample export, and the space in glass seal is sample chamber.
6. waveguide according to claim 5, is characterized in that: the material of upper strata metal film is silver, and the thickness of upper strata metal film is 35nm.
7. waveguide according to claim 7, is characterized in that: the material of glass seal is optical glass, and its thickness is about 500 μm.
8. waveguide according to claim 6, is characterized in that: the material of glass seal is optical glass, and its thickness is about 500 μm.
9. waveguide according to claim 7, is characterized in that: the material of lower metal film is silver, and its thickness is about 200nm.
10. waveguide according to claim 8, is characterized in that: the material of glass substrate is optical glass, and its thickness is 1000 μm.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510235554.4A CN105044042A (en) | 2015-05-08 | 2015-05-08 | Concentration detection method of manganese in trace amount in drinking water and waveguide used therein |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510235554.4A CN105044042A (en) | 2015-05-08 | 2015-05-08 | Concentration detection method of manganese in trace amount in drinking water and waveguide used therein |
Publications (1)
Publication Number | Publication Date |
---|---|
CN105044042A true CN105044042A (en) | 2015-11-11 |
Family
ID=54450757
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201510235554.4A Pending CN105044042A (en) | 2015-05-08 | 2015-05-08 | Concentration detection method of manganese in trace amount in drinking water and waveguide used therein |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN105044042A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105548093A (en) * | 2016-01-23 | 2016-05-04 | 宜春学院 | High-sensitivity oscillating field optical waveguide sensor |
CN107167452A (en) * | 2017-06-08 | 2017-09-15 | 复拓科学仪器(苏州)有限公司 | The stink damp body detecting method and detection means of waveguide are coated based on double-sided metal |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH10170427A (en) * | 1996-12-06 | 1998-06-26 | Shimadzu Corp | Detector cell and optical measurement device |
CN1595121A (en) * | 2004-06-24 | 2005-03-16 | 上海交通大学 | Optical waveguide biochemical sensor and measurement system based on free space coupling |
US7330263B2 (en) * | 2004-02-04 | 2008-02-12 | Fujifilm Corporation | Measurement method and apparatus |
WO2009091039A1 (en) * | 2008-01-16 | 2009-07-23 | Nippon Telegraph And Telephone Corporation | Surface plasmon resonance measuring device, sample cell, and measuring method |
-
2015
- 2015-05-08 CN CN201510235554.4A patent/CN105044042A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH10170427A (en) * | 1996-12-06 | 1998-06-26 | Shimadzu Corp | Detector cell and optical measurement device |
US7330263B2 (en) * | 2004-02-04 | 2008-02-12 | Fujifilm Corporation | Measurement method and apparatus |
CN1595121A (en) * | 2004-06-24 | 2005-03-16 | 上海交通大学 | Optical waveguide biochemical sensor and measurement system based on free space coupling |
WO2009091039A1 (en) * | 2008-01-16 | 2009-07-23 | Nippon Telegraph And Telephone Corporation | Surface plasmon resonance measuring device, sample cell, and measuring method |
Non-Patent Citations (5)
Title |
---|
刘爱平等: "水中锰[Ⅱ]的流动注射全自动在线分析", 《分析仪器》 * |
程晓宏: "液芯波导光度分析及其在食品安全中的应用", 《中国优秀硕士学位论文全文数据库 工程科技Ⅰ辑》 * |
管相宇等: "光波导共振技术结合比色法检测葡萄糖溶液的浓度", 《高等学校化学学报》 * |
陈先保等: "对称金属包覆光波导吸收传感器的研究", 《江西师范大学学报》 * |
陈发祥: "空心金属包覆波导检测小球藻溶液浓度的研究", 《安徽农业科学》 * |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105548093A (en) * | 2016-01-23 | 2016-05-04 | 宜春学院 | High-sensitivity oscillating field optical waveguide sensor |
CN107167452A (en) * | 2017-06-08 | 2017-09-15 | 复拓科学仪器(苏州)有限公司 | The stink damp body detecting method and detection means of waveguide are coated based on double-sided metal |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Worsfold et al. | Flow injection analysis as a tool for enhancing oceanographic nutrient measurements—A review | |
Wei et al. | Determination of phosphorus in natural waters by long-capillary-cell absorption spectrometry | |
Piraud et al. | An optoelectrochemical thin-film chlorine sensor employing evanescent fields on planar optical waveguides | |
Ogawa et al. | Determination of iron ion in the water of a natural hot spring using microfluidic paper-based analytical devices | |
JP2008224240A (en) | Attenuated total reflection probe and aqueous solution spectrometric device by using the same | |
CN107941710A (en) | Surface plasma resonance sensor and metal surface medium refraction index measuring method based on the weak measurement of quantum | |
US10677790B2 (en) | Optochemical detector and a method for fabricating an optochemical detector | |
Matsui et al. | Oxide Surface Plasmon Resonance for a New Sensing Platform in the Near‐Infrared Range | |
Geißler et al. | Evaluation of a ferrozine based autonomous in situ lab-on-chip analyzer for dissolved iron species in coastal waters | |
CN205374304U (en) | A waveguide that is arranged in drinking water trace manganese concentration detection | |
Choi et al. | Development of sulphide-selective optode membranes based on fluorescence quenching | |
CN105044042A (en) | Concentration detection method of manganese in trace amount in drinking water and waveguide used therein | |
US20090066957A1 (en) | Method and Apparatus for Sensing a Target Substance by Analysing Time Series of Said Target Substance | |
Liu et al. | Seasonal variability of the carbonate system and air–sea CO2 flux in the outer Changjiang Estuary, East China Sea | |
JP4372567B2 (en) | Method for measuring water and aqueous solution by ultraviolet light | |
Pourbasheer et al. | Design of a novel optical sensor for determination of trace amounts of copper by UV–visible spectrophotometry in real samples | |
Geißler et al. | Lab-on-chip analyser for the in situ determination of dissolved manganese in seawater | |
Oda et al. | Analysis of turbid solutions by laser-induced photoacoustic spectroscopy | |
JP4406702B2 (en) | Formaldehyde detection method and detection apparatus | |
Abanulo et al. | Waveguide surface plasmon resonance studies of surface reactions on gold electrodes | |
Jung et al. | Thickness dependence of surface plasmon resonance sensor response for metal ion detection | |
Powers et al. | Using liquid chromatography‐isotope ratio mass spectrometry to measure the δ13C of dissolved inorganic carbon photochemically produced from dissolved organic carbon | |
Wang et al. | Detection of mercury ion based on quantum dots using miniaturised optical fibre sensor | |
CN107167452A (en) | The stink damp body detecting method and detection means of waveguide are coated based on double-sided metal | |
Kim et al. | Investigation of a fiber optic surface plasmon spectroscopy in conjunction with conductivity as an in situ method for simultaneously monitoring changes in dissolved organic carbon and salinity in coastal waters |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20151111 |
|
RJ01 | Rejection of invention patent application after publication |