CN101576485A - Analytical method of multi-source spectrum fusion water quality - Google Patents

Analytical method of multi-source spectrum fusion water quality Download PDF

Info

Publication number
CN101576485A
CN101576485A CNA2009100993367A CN200910099336A CN101576485A CN 101576485 A CN101576485 A CN 101576485A CN A2009100993367 A CNA2009100993367 A CN A2009100993367A CN 200910099336 A CN200910099336 A CN 200910099336A CN 101576485 A CN101576485 A CN 101576485A
Authority
CN
China
Prior art keywords
centerdot
spectrum
model
water
signal
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
Application number
CNA2009100993367A
Other languages
Chinese (zh)
Inventor
吴铁军
单战虎
武晓莉
穆海洋
李艳君
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Zhejiang University ZJU
Original Assignee
Zhejiang University ZJU
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Zhejiang University ZJU filed Critical Zhejiang University ZJU
Priority to CNA2009100993367A priority Critical patent/CN101576485A/en
Publication of CN101576485A publication Critical patent/CN101576485A/en
Pending legal-status Critical Current

Links

Images

Abstract

The invention discloses an analytical method of multi-source spectrum fusion water quality. The method takes an ultraviolet/visible absorption spectrum signal and a multi-dimensional fluorescence emission spectrum signal of a water sample to be tested as input, and respectively adopts independent component pretreatment method to extract characteristic signals, remove interference information and obtain characteristic signals of the spectrums. According to the contribution of the characteristic signals of the spectrums to a water quality analyzing model, and aiming at avoiding information hiding, the combined characteristic signal number of the two types of spectrums is determined, the characteristic signals are combined into a spectrum characteristic signal federated data set, and the optimal spectrum configuration combination is solved. Based on an improved support vector machine algorithm, a Boosting method is adopted for modeling, and the optimal spectrum fusion water quality analyzing model is obtained by combining a plurality of modeling results. Based on the spectrum characteristic signal federated data set, the computation model is adopted to compute the comprehensive organic substance pollution index value of the water sample to be tested. The method has the remarkable advantages of high analyzing accuracy, high analysis speed, no pollution of chemical agent, simple operation and maintenance and the like.

Description

A kind of analytical method of multi-source spectrum fusion water quality
Technical field
The invention belongs to technical field of resource environments, be used for the fast detecting of water-quality guideline, be meant a kind of analytical method of multi-source spectrum fusion water quality especially.
Background technology
Comprehensive organic index (as TOC, COD, BOD, DOC, PAHs and permanganate index) is to weigh the important state definiteness mark of water pollution degree.
Traditional chemical analysis method is with a long history, technology maturation, analysis precision height, reliable results.But its analytical cycle length, secondary pollution, need shortcomings such as specialty analysis personnel operation, make this method or do not have to use under the situations such as specialty analysis personnel in the open air, more can cause second environmental pollution.
Have remarkable advantages such as no chemical reagent pollutes, analysis speed is fast based on the comprehensive organic index analysis method of the water quality of spectral analysis, developed fast in recent years.Existing these class methods mainly are based on ultraviolet/visible (UV/Vis) absorption spectrum or fluorescence excitation spectrum.
Ultra-violet absorption spectrum is used to estimate that organism comprehensive parameters such as TOC, COD have a lot of achievements in research, and existing portable analytical equipment comes into the market.China had issued uv absorption water quality automatic on-line monitoring instrument technical requirement (HJ/T 191-2005) in 2005, when pointing out that in water quality monitoring absorbance and COD or permanganate index have correlativity, UV absorption spectrum absorbance can be converted to COD or permanganate index, for road has been paved in the application of such optical analysis method in water analysis.But in fact,, disturb very big to absorption spectrum because inorganic suspension has stronger absorptivity to the UV/Vis light source; As adopt isolated by filtration, and can remove suspension simultaneously again, can't monitor true pollution condition; In addition, the UV absorptiometry is bigger to the extremely low organism analytical error of specific absorption coefficient, only is applicable to the water sample object that change of component is little.These shortcomings hinder the widespread use of water analysis instrument in extensive environmental monitoring system based on the UV absorption spectrum.
Fluorometry comprises synchronous fluorimetry, three-dimensional fluorescence method, derivative fluorescence method, time-resolved fluorescence method, differentiates fluorescence method, fluorescence kinetics method etc. mutually, what wherein have outstanding performance is that three-dimensional excites-the emitting fluorescence method, can intactly describe the fluorescent characteristics of material, be known as the spectral fingerprint technology of fluorescent material.American scholar utilized three-dimensional fluorescence that the dissolved organic carbon of NJ USA rainwash is monitored in 2004, and effect is better than single wavelength UV absorbance method [6].Beginning in 2003, the Chinese scholar also launched the research that fluorescence method is used for water analysis in succession, and organism has humic acid, dissolved organic matter, chlorophyll-a in the branch bleed.The shortcoming of fluorometry is easily affected by environment, there are labile factors such as cancellation, self-absorption, interior optical filtering in fluorescence itself, the spectral information (such as Raman spectrum) that directly except that fluorescence information, has also comprised water itself in the fluorescence data of measuring, and some other interference and noise information.
For this reason, the subject matter that solves in the subject study comprises the pre-service of high strength interfere information in the analysis water-like spectrum measuring data, the ultraviolet/visible absorption spectra of analysis water-like and the information fusion and the rapid modeling algorithm of multidimensional fluorescence emission spectrum, utilizes the organism parameter index of model solution water sample to be measured.
Summary of the invention
The objective of the invention is to overcome the deficiencies in the prior art, a kind of analytical method of multi-source spectrum fusion water quality is provided.
Analytical method of multi-source spectrum fusion water quality comprises the steps:
1),, produces ultraviolet/visible absorption spectra signal respectively by uviol lamp and integrated semiconductor laser irradiation for given water sample x 1 = { x 1,1 , x 1,2 , · · · , x 1 , s 1 } With multidimensional fluorescence emission spectrum signal
x 2 = { x 2,1 , x 2,2 , · · · , x 2 , s 2 } ;
2) adopt the statistical independence that comprises higher order statistical information to weigh the characteristic signal of extraction and the proximity of reference signal, by dual independent component analysis, structure denoise algorithm IICA-R carries out feature extraction to the training sample that is used for model modeling;
3) ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum signal with water sample is input, uses denoise algorithm, obtains the spectrum characteristics signal;
4) adopt k-to roll over the calculated performance of cross validation method evaluate spectra analytical model, find the solution best spectral signature signal configures combination;
5) construct algorithm of support vector machine LS-SVM fast, obtain the basic model of water analysis method;
6) adopting the Boosting method, is basic modeling algorithm with the LS-SVM algorithm, obtains best spectrum by the result who makes up repeatedly modeling and merges the water analysis model;
7) adopt spectrum to merge the water analysis model, on the basis of spectral signature combined signal data set, calculate the comprehensive organic pollutants desired value of water sample to be measured.
Described employing comprises the statistical independence of higher order statistical information and weighs the characteristic signal of extraction and the proximity of reference signal, by dual independent component analysis, structure denoise algorithm IICA-R, the training sample that is used for model modeling is carried out characteristic extraction step: adopt the statistical independence that comprises higher order statistical information to weigh the characteristic signal of extraction and the proximity of reference signal, use independent component to analyze ICA raw sample data X is extracted d characteristic signal: F=BX TConstitute set of variables F=[f 1..., f d] TBe the given new set of variables V=[F of organism overall target chemical analysis value y composition with F and reference signal then, y] T=[v 1..., v D+1] T, and V reused ICA, and: S=WV; Because at d characteristic signal f 1..., f dIn, exist a characteristic signal relevant at least with reference signal y, therefore ICA can only extract d independent component at the most for the second time; If the separation matrix that the second time, ICA tried to achieve is W=[w Ij] ∈ R D * (d+1), the new independent component of extraction is S=[s 1..., s d] TDefine independence measure index vector a: T=[t 1..., t i... t d] T, t i = arg max k = 1 , · · · , d { w ‾ ik } Set independence metric threshold θ ∈ (0,1); If
Figure A20091009933600082
t g>θ then thinks individual features variable f gWith y approach separate, can be with f gRegard the interfere information irrelevant as and rejected that remaining characteristic variable can be thought merging the effective characteristic information of modeling with merging modeling.
Described ultraviolet/visible absorption spectra and multidimensional fluorescence emission spectrum signal with water sample is input, uses denoise algorithm, obtains the spectrum characteristics signals step: with the ultraviolet/visible absorption spectra signal of water sample x 1 = { x 1,1 , x 1,2 , · · · , x 1 , s 1 } With multidimensional fluorescence emission spectrum signal x 2 = { x 2,1 , x 2,2 , · · · , x 2 , s 2 } Be input, use ICA tentatively to extract characteristic signal to X, order:
F=B·X=[f 1,…,f d] T
B ∈ R wherein D * pThe spectral signature separation matrix that obtains when using ICA for the first time for the spectrum water analysis model modeling stage, the characteristic signal of F for therefrom just selecting; Independence metric threshold θ is set, and calculates independence measure index t i, i=1,2 ..., d.All are satisfied t k<θ, k=k 1, k 2..., k n, the n of a n≤d characteristic signal constitutes water sample spectral signature signal vector F * = [ f k 1 , · · · , f k n ] T .
The calculated performance of described employing k-folding cross validation method evaluate spectra analytical model, find the solution best spectral signature signal configures combination step: be located at n and be used for setting up the sample that spectrum merges the water analysis model, the ultraviolet/visible absorption spectra of k water sample and the characteristic signal set of multidimensional fluorescence emission spectrum extraction are respectively z k 1 ( n 1 ) = { z k 1,1 , z k 1,2 , · · · , z k 1 , n 1 } With z k 2 ( n 2 ) = { z k 2,1 , z k 2,2 , · · · , z k 2 , n 2 } , N wherein 1And n 2Be respectively uv-visible absorption spectra and multidimensional fluorescence emission spectrum characteristic signal quantity; K the spectrum fusion water analysis model input vector that two kinds of spectral signature combined signals are constituted is z k(n 1, n 2)=[z K1(n 1), z K2(n 2)] T, remember that the water-quality guideline chemical analysis value of this water sample is y kBe located at sample set Θ (n 1, n 2)={ z k(n 1, n 2), y k} K=1,2 ..., nThe basis on, the spectrum of foundation merges the water analysis model and is:
y ^ = f ( z , Θ ( n 1 , n 2 ) )
Adopt the calculated performance of k-folding cross validation method assessment analysis of spectrum model, the set that is about to n sample be divided into randomly k mutually disjoint, big or small subclass about equally, set up the water analysis model with k-1 subclass wherein, utilize the performance of the analytical error root mean square assessment models of last remaining subclass.Repeat k time according to above process, so each subclass all has an opportunity to test, estimate to expect extensive error according to the mean value RMSEP of the RMSEP that obtains after k the iteration; For given n modeling water sample, obviously spectrum merges water analysis modular form RMSEP index and n 1And n 2Relevant; Therefore, can select best characteristic signal configuration combination by finding the solution of following optimization problem: min n 1 , n 2 RMSEP ‾ ( n 1 , n 2 )
Described utilization is algorithm of support vector machine LS-SVM fast, obtain the basic model step of water analysis method: with the ultraviolet/visible absorption spectra of water quality sample and the associating characteristic signal vector of multidimensional fluorescence emission spectrum is the input sample, with corresponding water sample organism overall target chemical analysis value is output sample, at sample set { z k, y k} K=1,2 ..., nThe basis on the LS-SVM algorithm can provide the water analysis basic model of following form:
y = Σ k = 1 n a k K ( z , z k ) + b
Wherein z is the ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum associating characteristic signal vector of water sample to be analyzed, z kBe the ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum associating characteristic signal vector of training water sample, y is the Model Calculation value of given organism overall target, and K is the kernel function that satisfies the Mercer condition.
Described employing Boosting method is basic modeling algorithm with the LS-SVM algorithm, obtains best spectrum by the result who makes up repeatedly modeling and merges water analysis model step:
(1) imports the sample set (z of nominalization 1, y 1) ..., (z n, y n); And initialization r=y, combination regression model F c=0, the combination regression model is to the match value of r r ^ c = 0 , Iterations m=1;
(2) to data set (z 1, r 1) ..., (z n, r n) use the modeling of LS-SVM algorithm, obtain basic regression model:
F ( z ) = Σ k = 1 n a m , k K ( z , z k ) + b m
A wherein M, k(k=1 ..., n) and b mBy following Solving Linear:
1 → n T a m = 0
1 → n T b m + ( Ω + γ - 1 I ) a m = r
Wherein 1 → n = [ 1 , · · · , 1 ] T , a m=[a m1,…,a mn] T
Figure A20091009933600098
k,l=1,…,n,K(x k,x l)
Be kernel function;
(3) calculate the weights β of basic regression model in this iteration m:
β m = ϵ | | r | | 2 | | r ^ | | 2
Wherein
Figure A200910099336000910
Be the match value of basic regression model F to r, and
ϵ = r · r ^ | | r | | 2 | | r ^ | | 2
(4) upgrade combination regression model F c
F c ( z ) ⇐ F c ( z ) + β m · F ( z )
(5) upgrade r = y - r ^ c , Wherein
Figure A20091009933600103
Be combination regression model F cMatch value to r;
(6) calculate iteration stopping desired value C m:
C m = 1 n | | y - r ^ c | | 2 + 1 2 | | | 1 n β m Σ m a m | | 2
If satisfy iteration stopping criterion C m>C M-1, (m>1) then algorithm stops; Otherwise return step (2), just can obtain best model.
The comprehensive organic pollutants desired value step of described calculating water sample to be measured: calculate the comprehensive organic pollutants desired value y of water sample to be measured on the basis of spectral signature combined signal data set z, computing formula is as follows:
y = Σ m = 1 N { β m · [ Σ k = 1 n a mk K ( z , z k ) + b m ] }
Wherein z is the ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum associating characteristic signal vector of water sample to be analyzed, z kBe the ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum associating characteristic signal vector of training water sample, y is the Model Calculation value of given organism overall target, and K is the kernel function that satisfies the Mercer condition, wherein β mBe the basic model weights that obtain after the m time Boosting iteration, a and b are model constants.
The present invention has set up mathematical model accurately, has realized that UV, visible light (UV/Vis) spectral analysis and emission spectrographic analyses such as fluorescence, Raman unite two into one, and information fusion has improved analysis precision.Can satisfy the on-the-spot express-analysis demand in daily and the outburst surroundings pollution monitoring work, can be used for the development research of corresponding instrument instrument.
Description of drawings
Fig. 1 is the analytical method of multi-source spectrum fusion water quality process flow diagram;
Fig. 2 is the Model Calculation value of multi-source optical spectrum convergence analysis model and the comparison synoptic diagram of measured value;
Fig. 3 is the Model Calculation value of multi-source optical spectrum convergence analysis model and the degree of correlation synoptic diagram of measured value.
Embodiment
Water analysis of the present invention is to liking surface water.Because the sampling position is changeable, also variation is bigger along with contaminated situation is different for the composition of water sample and each components contents.From the analytic target angle, there is the interference of suspension, colloidal materials and inorganic ions in the water sample to be analyzed, can have a strong impact on analysis precision.And these interference can not physical separation be removed, and also do not have clear and definite statistical nature, can't remove by general filter, must adopt other effective means to reduce and disturb the influence that brings.Existing denoising method or priori that need be more, there is irrationality in the setting of perhaps denoising mechanism, is not suitable for water quality spectral analysis research object; And feature extracting method is not to design for signal denoising specially, can not guarantee that the feature of extracting is effective to regression modeling.At this problem, the present invention proposes a kind of new denoising method that is applicable to this subject study object on the basis of ICA algorithm, be used for solving the denoising problem of water analysis higher-dimension spectroscopic data.
From the analysis tool angle, though single ultraviolet/visible absorption spectra or multidimensional fluorescence emission spectrometry can both divide the overall target of the organism in the bleed, but because existence and the intrinsic separately weak point of single spectrum disturbed are difficult to obtain desirable analysis precision.On the other hand, it is few and lack the characteristics of the priori of modeling that the water sample spectroscopic data has a sample size, therefore must select suitable modeling algorithm, to obtain the best model precision.It is theoretical at the best of small sample statistical estimate and Model Calculation study at present that Statistical Learning Theory is considered to, the support vector machine (SVM) of coming based on the Statistical Learning Theory development is to be specifically designed to a kind of modeling algorithm of small sample data, has good extensive performance, and solved the dimension disaster problem, can effectively handle high dimensional data.The LS-SVM algorithm is based on the improvement of regularization theory to standard SVM, be converted into the problem of finding the solution system of linear equations and don't change characteristics such as original kernel function mapping relations and global optimum finding the solution quadratic programming problem among the SVM, therefore when guaranteeing model performance, greatly reduce the computation complexity of SVM, have arithmetic speed faster.The present invention proposes a kind of water analysis method based on the multi-source optical spectrum information fusion, adopts the Boosting method, is basic modeling algorithm with the LS-SVM algorithm, obtains best spectrum by the result who makes up repeatedly modeling and merges the water analysis model.So, can realize the selection and the information balance of spectral information amalgamation mode, thereby improve the Model Calculation precision of organic parameter.
Analytical method of multi-source spectrum fusion water quality comprises the steps:
1),, produces ultraviolet/visible absorption spectra signal respectively by uviol lamp and integrated semiconductor laser irradiation for given water sample x 1 = { x 1,1 , x 1 , 2 , · · · , x 1 , s 1 } With multidimensional fluorescence emission spectrum signal
x 2 = { x 2,1 , x 2,2 , · · · , x 2 , s 2 } ;
2) adopt the statistical independence that comprises higher order statistical information to weigh the characteristic signal of extraction and the proximity of reference signal, by dual independent component analysis, structure denoise algorithm IICA-R carries out feature extraction to the training sample that is used for model modeling;
3) ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum signal with water sample is input, uses denoise algorithm, obtains the spectrum characteristics signal;
4) adopt k-to roll over the calculated performance of cross validation method evaluate spectra analytical model, find the solution best spectral signature signal configures combination;
5) construct algorithm of support vector machine LS-SVM fast, obtain the basic model of water analysis method;
6) adopting the Boosting method, is basic modeling algorithm with the LS-SVM algorithm, obtains best spectrum by the result who makes up repeatedly modeling and merges the water analysis model;
7) adopt spectrum to merge the water analysis model, on the basis of spectral signature combined signal data set, calculate the comprehensive organic pollutants desired value of water sample to be measured.
Described employing comprises the statistical independence of higher order statistical information and weighs the characteristic signal of extraction and the proximity of reference signal, by dual independent component analysis, structure denoise algorithm IICA-R, the training sample that is used for model modeling is carried out characteristic extraction step: adopt the statistical independence that comprises higher order statistical information to weigh the characteristic signal of extraction and the proximity of reference signal, use independent component to analyze ICA raw sample data X is extracted d characteristic signal: F=BX TConstitute set of variables F=[f 1..., f d] TBe the given new set of variables V=[F of organism overall target chemical analysis value y composition with F and reference signal then, y] T=[v 1..., v D+1] T, and V reused ICA, and: S=WV; Because at d characteristic signal f 1..., f dIn, exist a characteristic signal relevant at least with reference signal y, therefore ICA can only extract d independent component at the most for the second time; If the separation matrix that the second time, ICA tried to achieve is W=[w Ij] ∈ R D * (d+1), the new independent component of extraction is S=[s 1..., s d] TDefine independence measure index vector a: T=[t 1..., t i... t d] T, t i = arg max k = 1 , · · · , d { w ‾ ik } Set independence metric threshold θ ∈ (0,1); If
Figure A20091009933600122
t g>θ then thinks individual features variable f gWith y approach separate, can be with f gRegard the interfere information irrelevant as and rejected that remaining characteristic variable can be thought merging the effective characteristic information of modeling with merging modeling.
Described ultraviolet/visible absorption spectra and multidimensional fluorescence emission spectrum signal with water sample is input, uses denoise algorithm, obtains the spectrum characteristics signals step: with the ultraviolet/visible absorption spectra signal of water sample x 1 = { x 1,1 , x 1,2 , · · · , x 1 , s 1 } With multidimensional fluorescence emission spectrum signal x 2 = { x 2,1 , x 2,2 , · · · , x 2 , s 2 } Be input, use ICA tentatively to extract characteristic signal to X, order:
F=B·X=[f 1,…,f d] T
B ∈ R wherein D * pThe spectral signature separation matrix that obtains when using ICA for the first time for the spectrum water analysis model modeling stage, the characteristic signal of F for therefrom just selecting; Independence metric threshold θ is set, and calculates independence measure index t i, i=1,2 ..., d.All are satisfied t k<θ, k=k 1, k 2..., k n, the n of a n≤d characteristic signal constitutes water sample spectral signature signal vector F * = [ f k 1 , · · · , f k n ] T .
The calculated performance of described employing k-folding cross validation method evaluate spectra analytical model, find the solution best spectral signature signal configures combination step: be located at n and be used for setting up the sample that spectrum merges the water analysis model, the ultraviolet/visible absorption spectra of k water sample and the characteristic signal set of multidimensional fluorescence emission spectrum extraction are respectively z k 1 ( n 1 ) = { z k 1,1 , z k 1,2 , · · · , z k 1 , n 1 } With z k 2 ( n 2 ) = { z k 2,1 , z k 2,2 , · · · , z k 2 , n 2 } , N wherein 1And n 2Be respectively uv-visible absorption spectra and multidimensional fluorescence emission spectrum characteristic signal quantity; K the spectrum fusion water analysis model input vector that two kinds of spectral signature combined signals are constituted is z k(n 1, n 2)=[z K1(n 1), z K2(n 2)] T, remember that the water-quality guideline chemical analysis value of this water sample is y kBe located at sample set Θ (n 1, n 2)={ z k(n 1, n 2), y k} K=1,2 ..., nThe basis on, the spectrum of foundation merges the water analysis model and is:
y ^ = f ( z , Θ ( n 1 , n 2 ) )
Adopt the calculated performance of k-folding cross validation method assessment analysis of spectrum model, the set that is about to n sample be divided into randomly k mutually disjoint, big or small subclass about equally, set up the water analysis model with k-1 subclass wherein, utilize the performance of the analytical error root mean square assessment models of last remaining subclass.Repeat k time according to above process, so each subclass all has an opportunity to test, estimate to expect extensive error according to the mean value RMSEP of the RMSEP that obtains after k the iteration; For given n modeling water sample, obviously spectrum merges water analysis modular form RMSEP index and n 1And n 2Relevant; Therefore, can select best characteristic signal configuration combination by finding the solution of following optimization problem: min n 1 , n 2 RMSEP ‾ ( n 1 , n 2 )
Described utilization is algorithm of support vector machine LS-SVM fast, obtain the basic model step of water analysis method: with the ultraviolet/visible absorption spectra of water quality sample and the associating characteristic signal vector of multidimensional fluorescence emission spectrum is the input sample, with corresponding water sample organism overall target chemical analysis value is output sample, at sample set { z k, y k} K=1,2 ..., nThe basis on the LS-SVM algorithm can provide the water analysis basic model of following form:
y = Σ k = 1 n a k K ( z , z k ) + b
Wherein z is the ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum associating characteristic signal vector of water sample to be analyzed, z kBe the ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum associating characteristic signal vector of training water sample, y is the Model Calculation value of given organism overall target, and K is the kernel function that satisfies the Mercer condition.
Described employing Boosting method is basic modeling algorithm with the LS-SVM algorithm, obtains best spectrum by the result who makes up repeatedly modeling and merges water analysis model step:
(1) imports the sample set (z of nominalization 1, y 1) ..., (z n, y n); And initialization r=y, combination regression model F c=0, the combination regression model is to the match value of r r ^ c = 0 , Iterations m=1;
(2) to data set (z 1, r 1) ..., (z n, r n) use the modeling of LS-SVM algorithm, obtain basic regression model:
F ( z ) = Σ k = 1 n a m , k K ( z , z k ) + b m
A wherein M, k(k=1 ..., n) and b mBy following Solving Linear:
1 → n T a m = 0
1 → n T b m + ( Ω + γ - 1 I ) a m = r
Wherein 1 → n = [ 1 , · · · , 1 ] T , a m=[a M1..., a Mn] T,
Figure A20091009933600138
K, l=1 ..., n, K (x k, x l) be kernel function;
(3) calculate the weights β of basic regression model in this iteration m:
β m = ϵ | | r | | 2 | | r ^ | | 2
Wherein
Figure A20091009933600142
Be the match value of basic regression model F to r, and
ϵ = r · r ^ | | r | | 2 | | r ^ | | 2
(4) upgrade combination regression model F c
F c ( z ) ⇐ F c ( z ) + β m · F ( z )
(5) upgrade r = y - r ^ c , Wherein
Figure A20091009933600146
Be combination regression model F cMatch value to r;
(6) calculate iteration stopping desired value C m:
C m = 1 n | | y - r ^ c | | 2 + 1 2 | | | 1 n β m Σ m a m | | 2
If satisfy iteration stopping criterion C m>C M-1(m>1) then algorithm stops; Otherwise return step (2), just can obtain best model.
The comprehensive organic pollutants desired value step of described calculating water sample to be measured: calculate the comprehensive organic pollutants desired value y of water sample to be measured on the basis of spectral signature combined signal data set z, computing formula is as follows:
y = Σ m = 1 N { β m · [ Σ k = 1 n a mk K ( z , z k ) + b m ] }
Wherein z is the ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum associating characteristic signal vector of water sample to be analyzed, z kBe the ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum associating characteristic signal vector of training water sample, y is the Model Calculation value of given organism overall target, and K is the kernel function that satisfies the Mercer condition, wherein β mBe the basic model weights that obtain after the m time Boosting iteration, a and b are model constants.
By a large amount of experiments, checked the validity of above-mentioned analytical method of multi-source spectrum fusion water quality.Be noted that: for the analysis of each given water quality organism overall target, all need on same water sample ultraviolet/visible absorption spectra and multidimensional fluorescence emission spectrum measuring-signal basis, according to corresponding organism overall target chemical analysis value, setting up independently, spectrum merges the water analysis model.But say from methodology, above-mentioned analytical method of multi-source spectrum fusion water quality merges the water analysis model to the spectrum of each given organism overall target and all is suitable for, the concrete adjustment but the various algorithm parameters that relate in modeling and the analytical calculation process then need according to different analysis purposes.
It is example that the multi-source optical spectrum of one of water quality organism overall target---TOC merges water analysis, and the experiment results about analytical method of multi-source spectrum fusion water quality validity is described.Surface water water sample with one group of Hangzhou is an example, and following table has been listed the TOC chemical analysis value of this group water sample:
The water sample numbering TOC (mg/L) The water sample numbering TOC (mg/L) The water sample numbering TOC (mg/L) The water sample numbering TOC (mg/L)
1 6.93 9 82.46 17 49.17 25 29.35
2 16.20 10 27.74 18 43.25 26 80.43
3 14.69 11 25.67 19 29.07 27 26.94
4 11.77 12 27.79 20 14.98 28 51.07
5 17.06 13 33.54 21 76.79 29 64.74
6 3.41 14 53.74 22 95.49 30 67.09
7 8.04 15 78.29 23 125.30 31 63.98
8 13.10 16 54.58 24 49.46 32 59.48
Use the multi-source optical spectrum analytical approach then, simple steps is as follows:
Step 1: the spectrum that generates water sample to be measured.
For given water sample,, produce ultraviolet/visible absorption spectra and multidimensional fluorescence emission spectrum signal respectively by the light source irradiation of certain intensity and wavelength x 1 = { x 1,1 , x 1,2 , · · · , x 1 , s 1 } With x 2 = { x 2,1 , x 2,2 , · · · , x 2 , s 2 } .
Step 2: the spectral signature signal that extracts water sample to be measured.
To water sample ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum signal that obtains, adopt the IICA-R Signal Pre-Processing Method to extract characteristic signal respectively, remove interfere information, obtain the spectral signature signal z 1 = { z 1,1 , z 1,2 , · · · , z 1 , n 1 } With z 2 = { z 2,1 , z 2,2 , · · · , z 2 , n 2 } .
Step 3: the spectral signature signal that makes up water sample to be measured.
According to the contribution of pretreated water sample ultraviolet/visible absorption spectra to be measured and multidimensional fluorescence emission spectrum characteristic signal to the water analysis model, be the definite two class spectral signature number of signals that make up of target to avoid information to cover, and be combined into spectral signature combined signal data set z = [ z ‾ 1 , z ‾ 2 ] T ∈ R n ‾ 1 + n ‾ 2 .
Step 4: the spectrum convergence analysis value of calculating water sample to be measured.
Adopt spectrum to merge the water analysis model, on the basis of spectral signature combined signal data set z, calculate the comprehensive organic pollutants desired value y of water sample to be measured.
Fig. 3 and Fig. 4 provide respectively adopt the IICA-R method that two kinds of spectrum independently are extracted feature and the characteristic signal number combinations of the best is set after the The model calculation of Boosting-LS-SVM institute established model, and the correlative relationship figure of Model Calculation value and assay value.As can be seen, the IICA-R method that adopts this problem to propose is extracted feature and the spectrum of setting up after the best characteristic signal number combinations is set and merges the water analysis model, Model Calculation value to water sample TOC parameter can be good at approaching the chemical measurement value, the linear dependence degree height of the two.This shows that the water analysis method that multi-source optical spectrum merges has excellent application value, is the another kind of method of analyzing water pollution, has remarkable advantages such as analysis precision height, fast, the no chemical reagent pollution of analysis speed, Operation and Maintenance be simple.

Claims (7)

1, a kind of analytical method of multi-source spectrum fusion water quality is characterized in that comprising the steps:
1),, produces ultraviolet/visible absorption spectra signal respectively by uviol lamp and integrated semiconductor laser irradiation for given water sample x 1 = { x 1,1 , x 1,2 , · · · , x 1 , s 1 } With multidimensional fluorescence emission spectrum signal
x 2 = { x 2,1 , x 2,2 , · · · , x 2 , s 2 } ;
2) adopt the statistical independence that comprises higher order statistical information to weigh the characteristic signal of extraction and the proximity of reference signal, by dual independent component analysis, structure denoise algorithm IICA-R carries out feature extraction to the training sample that is used for model modeling;
3) ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum signal with water sample is input, uses denoise algorithm, obtains the spectrum characteristics signal;
4) adopt k-to roll over the calculated performance of cross validation method evaluate spectra analytical model, find the solution best spectral signature signal configures combination;
5) construct algorithm of support vector machine LS-SVM fast, obtain the basic model of water analysis method;
6) adopting the Boosting method, is basic modeling algorithm with the LS-SVM algorithm, obtains best spectrum by the result who makes up repeatedly modeling and merges the water analysis model;
7) adopt spectrum to merge the water analysis model, on the basis of spectral signature combined signal data set, calculate the comprehensive organic pollutants desired value of water sample to be measured.
2. a kind of analytical method of multi-source spectrum fusion water quality according to claim 1, it is characterized in that the statistical independence that described employing comprises higher order statistical information weighs the characteristic signal of extraction and the proximity of reference signal, by dual independent component analysis, structure denoise algorithm IICA-R, the training sample that is used for model modeling is carried out characteristic extraction step: adopt the statistical independence that comprises higher order statistical information to weigh the characteristic signal of extraction and the proximity of reference signal, use independent component to analyze ICA raw sample data X is extracted d characteristic signal: F=BX TConstitute set of variables F=[f 1..., f d] TBe the given new set of variables V=[F of organism overall target chemical analysis value y composition with F and reference signal then, y] T=[v 1..., v D+1] T, and V reused ICA, and: S=WV; Because at d characteristic signal f 1..., f dIn, exist a characteristic signal relevant at least with reference signal y, therefore ICA can only extract d independent component at the most for the second time; If the separation matrix that the second time, ICA tried to achieve is W=[w Ij] ∈ R D * (d+1), the new independent component of extraction is S=[s 1..., s d] TDefine independence measure index vector a: T=[t 1..., t i... t d] T, t i = arg max k = 1 , · · · , d { w ‾ ik } Set independence metric threshold θ ∈ (0,1); If t g>θ then thinks individual features variable f gWith y approach separate, can be with f gRegard the interfere information irrelevant as and rejected that remaining characteristic variable can be thought merging the effective characteristic information of modeling with merging modeling.
3. a kind of analytical method of multi-source spectrum fusion water quality according to claim 1, it is characterized in that described ultraviolet/visible absorption spectra and multidimensional fluorescence emission spectrum signal with water sample is input, use denoise algorithm, obtain the spectrum characteristics signals step: with the ultraviolet/visible absorption spectra signal of water sample x 1 = { x 1,1 , x 1,2 , · · · , x 1 , s 1 } With multidimensional fluorescence emission spectrum signal x 2 = { x 2,1 , x 2,2 , · · · , x 2 , s 2 } Be input, use ICA tentatively to extract characteristic signal to X, order:
F=B·X=[f 1,…,f d] T
B ∈ R wherein D * pThe spectral signature separation matrix that obtains when using ICA for the first time for the spectrum water analysis model modeling stage, the characteristic signal of F for therefrom just selecting; Independence metric threshold θ is set, and calculates independence measure index t i, i=1,2 ..., d.All are satisfied t k<θ, k=k 1, k 2..., k n, the n of a n≤d characteristic signal constitutes water sample spectral signature signal vector F * = [ f k 1 , · · · , f k n ] T .
4. a kind of analytical method of multi-source spectrum fusion water quality according to claim 1, the calculated performance that it is characterized in that described employing k-folding cross validation method evaluate spectra analytical model, find the solution best spectral signature signal configures combination step: be located at n and be used for setting up the sample that spectrum merges the water analysis model, the ultraviolet/visible absorption spectra of k water sample and the characteristic signal set of multidimensional fluorescence emission spectrum extraction are respectively z k 1 ( n 1 ) = { z k 1,1 , z k 1,2 , · · · , z k 1 , n 1 } With z k 2 ( n 2 ) = { z k 2,1 , z k 2,2 , · · · , z k 2 , n 2 } , N wherein 1And n 2Be respectively uv-visible absorption spectra and multidimensional fluorescence emission spectrum characteristic signal quantity; K the spectrum fusion water analysis model input vector that two kinds of spectral signature combined signals are constituted is z k(n 1, n 2)=[z K1(n 1), z K2(n 2)] T, remember that the water-quality guideline chemical analysis value of this water sample is y kBe located at sample set Θ (n 1, n 2)={ z k(n 1, n 2), y k} K=1,2 ..., nThe basis on, the spectrum of foundation merges the water analysis model and is:
y ^ = f ( z , Θ ( n 1 , n 2 ) )
Adopt the calculated performance of k-folding cross validation method assessment analysis of spectrum model, the set that is about to n sample be divided into randomly k mutually disjoint, big or small subclass about equally, set up the water analysis model with k-1 subclass wherein, utilize the performance of the analytical error root mean square assessment models of last remaining subclass.Repeat k time according to above process, so each subclass all has an opportunity to test, estimate to expect extensive error according to the mean value RMSEP of the RMSEP that obtains after k the iteration; For given n modeling water sample, obviously spectrum merges water analysis modular form RMSEP index and n 1And n 2Relevant; Therefore, can select best characteristic signal configuration combination by finding the solution of following optimization problem:
Figure A2009100993360003C7
5. a kind of analytical method of multi-source spectrum fusion water quality according to claim 1, it is characterized in that described utilization algorithm of support vector machine LS-SVM fast, obtain the basic model step of water analysis method: with the ultraviolet/visible absorption spectra of water quality sample and the associating characteristic signal vector of multidimensional fluorescence emission spectrum is the input sample, with corresponding water sample organism overall target chemical analysis value is output sample, at sample set { z k, y k} K=1,2 ..., nThe basis on the LS-SVM algorithm can provide the water analysis basic model of following form:
y = Σ k = 1 n a k K ( z , z k ) + b
Wherein z is the ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum associating characteristic signal vector of water sample to be analyzed, z kBe the ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum associating characteristic signal vector of training water sample, y is the Model Calculation value of given organism overall target, and K is the kernel function that satisfies the Mercer condition.
6. a kind of analytical method of multi-source spectrum fusion water quality according to claim 1, it is characterized in that described employing Boosting method, with the LS-SVM algorithm is basic modeling algorithm, obtains best spectrum by the result who makes up repeatedly modeling and merges water analysis model step:
(1) imports the sample set (z of nominalization 1, y 1) ..., (z n, y n); And initialization r=y, combination regression model F c=0, the combination regression model is to the match value of r r ^ c = 0 , Iterations m=1;
(2) to data set (z 1, r 1) ..., (z n, r n) use the modeling of LS-SVM algorithm, obtain basic regression model:
F ( z ) = Σ k = 1 n a m , k K ( z , z k ) + b m
A wherein M, k(k=1 ..., n) and b mBy following Solving Linear:
1 → n T a m = 0
1 → n T b m + ( Ω + γ - 1 I ) a m = r
Wherein 1 → n = [ 1 , · · · , 1 ] T , a m=[a M1..., a Mn] T,
Figure A2009100993360004C7
K, l=1 ..., n, K (x k, x l) be kernel function;
(3) calculate the weights β of basic regression model in this iteration m:
β m = ϵ | | r | | 2 | | r ^ | | 2
Wherein
Figure A2009100993360004C9
Be the match value of basic regression model F to r, and
ϵ = r · r ^ | | r | | 2 | | r ^ | | 2
(4) upgrade combination regression model F c
F c ( z ) ⇐ F c ( z ) + β m · F ( z )
(5) upgrade r = y - r ^ c , Wherein Be combination regression model F cMatch value to r;
(6) calculate iteration stopping desired value C m:
C m = 1 n | | y - r ^ c | | 2 + 1 2 | | | 1 n β m Σ m a m | | 2
If satisfy iteration stopping criterion C m>C M-1, (m>1) then algorithm stops; Otherwise return step (2), just can obtain best model.
7. a kind of analytical method of multi-source spectrum fusion water quality according to claim 1, the comprehensive organic pollutants desired value step that it is characterized in that described calculating water sample to be measured: calculate the comprehensive organic pollutants desired value y of water sample to be measured on the basis of spectral signature combined signal data set z, computing formula is as follows:
y = Σ m = 1 N { β m · [ Σ k = 1 n a mk K ( z , z k ) + b m ] }
Wherein z is the ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum associating characteristic signal vector of water sample to be analyzed, z kBe the ultraviolet/visible absorption spectra and the multidimensional fluorescence emission spectrum associating characteristic signal vector of training water sample, y is the Model Calculation value of given organism overall target, and K is the kernel function that satisfies the Mercer condition, wherein β mBe the basic model weights that obtain after the m time Boosting iteration, a and b are model constants.
CNA2009100993367A 2009-06-04 2009-06-04 Analytical method of multi-source spectrum fusion water quality Pending CN101576485A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNA2009100993367A CN101576485A (en) 2009-06-04 2009-06-04 Analytical method of multi-source spectrum fusion water quality

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNA2009100993367A CN101576485A (en) 2009-06-04 2009-06-04 Analytical method of multi-source spectrum fusion water quality

Publications (1)

Publication Number Publication Date
CN101576485A true CN101576485A (en) 2009-11-11

Family

ID=41271476

Family Applications (1)

Application Number Title Priority Date Filing Date
CNA2009100993367A Pending CN101576485A (en) 2009-06-04 2009-06-04 Analytical method of multi-source spectrum fusion water quality

Country Status (1)

Country Link
CN (1) CN101576485A (en)

Cited By (18)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102661923A (en) * 2012-05-03 2012-09-12 四川碧朗科技有限公司 Complex monitor for automatically monitoring multiple parameters of water on line
CN106290276A (en) * 2016-08-01 2017-01-04 江苏大学 A kind of quality evaluation method of enclosed waters aquiculture fresh water
CN108108889A (en) * 2017-12-18 2018-06-01 杭州电子科技大学 A kind of water monitoring data on-line processing method and device
CN108507955A (en) * 2018-03-22 2018-09-07 上海交通大学 The device and method of multispectral synchronous detection chemical oxygen demand of water body
CN108801950A (en) * 2018-05-21 2018-11-13 东南大学 A kind of ultraviolet spectra abnormal water detection method based on sliding window Multiscale Principal Component Analysis
CN108956496A (en) * 2018-07-11 2018-12-07 东盛科兴环保科技河北有限公司 A kind of multi-wavelength detection method of rapid-digestion COD
CN109470667A (en) * 2018-11-14 2019-03-15 华东理工大学 A kind of combination water quality parameter and three-dimensional fluorescence spectrum carry out the method that pollutant is traced to the source
CN109752364A (en) * 2019-03-11 2019-05-14 广西科技大学 The asynchronous colour fading fluorescence elimination method of multicomponent system Raman spectrum
CN110456348A (en) * 2019-08-19 2019-11-15 中国石油大学(华东) The wave cut-off wavelength compensation method of more visual direction SAR ocean wave spectrum data fusions
CN111157485A (en) * 2019-12-19 2020-05-15 郑州轻工业大学 Rapid water quality detection device and detection method thereof
CN111239105A (en) * 2020-02-20 2020-06-05 南京信息工程大学 Spectrum monitoring system for sewage real-time monitoring
CN111487213A (en) * 2020-04-29 2020-08-04 武汉新烽光电股份有限公司 Multispectral fusion chemical oxygen demand testing method and device
CN111523582A (en) * 2020-04-16 2020-08-11 厦门大学 Trans-instrument Raman spectrum qualitative analysis method based on transfer learning
CN111982878A (en) * 2020-08-24 2020-11-24 安徽思环科技有限公司 Water pollution analysis method based on ultraviolet visible spectrum and three-dimensional fluorescence spectrum
CN112881353A (en) * 2021-01-11 2021-06-01 江西师范大学 Method and device for measuring concentration of soluble organic carbon in water body
CN113109287A (en) * 2021-03-17 2021-07-13 杭州兰亮网络科技有限公司 Detection method for obtaining image processing oil quality by additionally arranging sensor
CN114136900A (en) * 2021-11-03 2022-03-04 江苏省扬州环境监测中心 Water quality detection method combining ultraviolet visible light absorption spectrum technology
CN115684059A (en) * 2023-01-04 2023-02-03 中国市政工程华北设计研究总院有限公司 Method and system for detecting water body based on multiple spectra

Cited By (23)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102661923A (en) * 2012-05-03 2012-09-12 四川碧朗科技有限公司 Complex monitor for automatically monitoring multiple parameters of water on line
CN106290276A (en) * 2016-08-01 2017-01-04 江苏大学 A kind of quality evaluation method of enclosed waters aquiculture fresh water
CN108108889A (en) * 2017-12-18 2018-06-01 杭州电子科技大学 A kind of water monitoring data on-line processing method and device
CN108507955A (en) * 2018-03-22 2018-09-07 上海交通大学 The device and method of multispectral synchronous detection chemical oxygen demand of water body
CN108801950B (en) * 2018-05-21 2020-09-11 东南大学 Ultraviolet spectrum water quality abnormity detection method based on sliding window multi-scale principal component analysis
CN108801950A (en) * 2018-05-21 2018-11-13 东南大学 A kind of ultraviolet spectra abnormal water detection method based on sliding window Multiscale Principal Component Analysis
CN108956496A (en) * 2018-07-11 2018-12-07 东盛科兴环保科技河北有限公司 A kind of multi-wavelength detection method of rapid-digestion COD
CN109470667A (en) * 2018-11-14 2019-03-15 华东理工大学 A kind of combination water quality parameter and three-dimensional fluorescence spectrum carry out the method that pollutant is traced to the source
CN109752364A (en) * 2019-03-11 2019-05-14 广西科技大学 The asynchronous colour fading fluorescence elimination method of multicomponent system Raman spectrum
CN109752364B (en) * 2019-03-11 2021-06-08 广西科技大学 Asynchronous fading fluorescence elimination method of multi-component system Raman spectrum
CN110456348A (en) * 2019-08-19 2019-11-15 中国石油大学(华东) The wave cut-off wavelength compensation method of more visual direction SAR ocean wave spectrum data fusions
CN111157485A (en) * 2019-12-19 2020-05-15 郑州轻工业大学 Rapid water quality detection device and detection method thereof
CN111239105A (en) * 2020-02-20 2020-06-05 南京信息工程大学 Spectrum monitoring system for sewage real-time monitoring
CN111239105B (en) * 2020-02-20 2023-01-24 南京信息工程大学 Spectrum monitoring system for sewage real-time monitoring
CN111523582A (en) * 2020-04-16 2020-08-11 厦门大学 Trans-instrument Raman spectrum qualitative analysis method based on transfer learning
CN111523582B (en) * 2020-04-16 2023-05-12 厦门大学 Cross-instrument Raman spectrum qualitative analysis method based on transfer learning
CN111487213A (en) * 2020-04-29 2020-08-04 武汉新烽光电股份有限公司 Multispectral fusion chemical oxygen demand testing method and device
CN111982878A (en) * 2020-08-24 2020-11-24 安徽思环科技有限公司 Water pollution analysis method based on ultraviolet visible spectrum and three-dimensional fluorescence spectrum
CN112881353A (en) * 2021-01-11 2021-06-01 江西师范大学 Method and device for measuring concentration of soluble organic carbon in water body
CN113109287A (en) * 2021-03-17 2021-07-13 杭州兰亮网络科技有限公司 Detection method for obtaining image processing oil quality by additionally arranging sensor
CN114136900A (en) * 2021-11-03 2022-03-04 江苏省扬州环境监测中心 Water quality detection method combining ultraviolet visible light absorption spectrum technology
CN114136900B (en) * 2021-11-03 2024-04-09 江苏省扬州环境监测中心 Water quality detection method combining ultraviolet and visible light absorption spectrum technology
CN115684059A (en) * 2023-01-04 2023-02-03 中国市政工程华北设计研究总院有限公司 Method and system for detecting water body based on multiple spectra

Similar Documents

Publication Publication Date Title
CN101576485A (en) Analytical method of multi-source spectrum fusion water quality
Guo et al. Advances on water quality detection by uv-vis spectroscopy
CN107478580B (en) Soil heavy metal content estimation method and device based on hyperspectral remote sensing
CN114424058A (en) Tracing method for VOCs pollution
CN103983595B (en) A kind of water turbidity calculation method processed based on ultraviolet-visible spectrum
WO2020133944A1 (en) Method for constructing water quality index prediction model, and method for monitoring water quality index
CN102608061B (en) Improved method for extracting Fourier transformation infrared spectrum characteristic variable of multi-component gas by aid of TR (Tikhonov regularization)
CN103983617A (en) Improved laser probe quantitative analysis method based on wavelet transform
CN104596957A (en) Estimation method for content of copper in soil on basis of visible-light near-infrared spectrum technology
CN102254175B (en) Clustering analysis method for soil of different regions based on x-ray fluorescence spectrums
CN105044050A (en) Rapid quantitative analysis method for metallic elements in crop straw
CN106918565A (en) Heavy metal-polluted soil Cd contents Inverse modeling and its spectral response characteristics wave band recognition methods based on indoor standard specimen bloom spectrum signature
CN103293118A (en) Hogwash oil identification method based on near infrared reflectance spectroscopy
CN107462535A (en) A kind of spectrum resolution algorithm based on Gaussian rough surface
CN105486655A (en) Rapid detection method for organic matters in soil based on infrared spectroscopic intelligent identification model
CN102928396A (en) Urea isotopic abundance rapid detection method based on Raman spectrum
CN105468926A (en) Underground water type drinking water source pollution source analysis method
CN106770015A (en) A kind of oil property detection method based on the similar differentiation of principal component analysis
CN103175805A (en) Method for determining indexes of COD and BOD5 in sewage through near infrared spectrometry
CN105510427B (en) A kind of Numerical Methods for multiple element isotope double spike technology
CN101339150A (en) Method for determining octane number based on dielectric spectra technology
CN105044054A (en) Ocean oil spill fine telemetering method based on blind source separation
CN106126879B (en) A kind of soil near-infrared spectrum analysis prediction technique based on rarefaction representation technology
Torres et al. Local calibration for a UV/Vis spectrometer: PLS vs. SVM. A case study in a WWTP
CN105277531A (en) Grading-based coal characteristic measurement method

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Open date: 20091111