CN118817635B - Multispectral channel gas classification and quantitative detection method and system thereof - Google Patents
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Abstract
The invention belongs to the field of optical gas imaging detection, and discloses a multi-spectral channel gas classification and quantitative detection method and a system thereof, wherein an incident beam is divided into a plurality of sub-beams and filtered to obtain N-1 sub-beams with different narrowband spectral bands and a broadband all-pass band sub-beam; the method comprises the steps of converting sub-beams of N wave bands into digital image signals of multi-band channels for simultaneous imaging, carrying out image registration alignment on the digital image signals of the multi-band channels for simultaneous imaging and images of different channels, outputting a spectrum image cube, carrying out classification detection on the spectrum image cube to obtain pixel coordinate areas and type information of gas distribution, carrying out concentration equation quantitative calculation on the pixel coordinate areas and the type information of the gas distribution, carrying out pseudo-color enhancement on the gas, and outputting spatial distribution of gas concentration. The invention can obviously improve the application level of the optical gas detection technology and provide a more accurate and reliable solution for the fields of environmental monitoring and the like.
Description
Technical Field
The invention relates to the field of optical gas imaging detection, in particular to a multispectral channel gas classification and quantitative detection method and a multispectral channel gas classification and quantitative detection system.
Background
Optical gas imaging detection technology has been widely used in the fields of environmental monitoring, industrial process control, medical health, etc. in recent years due to its characteristics of non-invasiveness, high sensitivity, and imaging and real-time response. Conventional optical gas detection methods are based primarily on the light absorption properties of gas molecules, and infer the presence and concentration of a gas by measuring the absorption intensity at a single specific wavelength. However, these methods have exposed many problems in practical use, particularly when applied to chemical sites, it is difficult to accurately distinguish the kind of leakage gas and quantify the concentration thereof. When the leaking gas is of unknown kind, conventional single wavelength or narrow band light absorption techniques are struggling to cope with this complex situation. Single wavelength detection makes it difficult to distinguish between individual gas components because the absorption spectra of different gases may overlap at certain wavelengths. In this case, error accumulation leads to inaccurate detection results, and even missing detection or false alarm may occur. In addition to the identification of gas species, accurate measurement of gas concentrations is also a challenge in optical gas detection techniques. There is no optical gas imaging detection technology capable of achieving concentration quantification in the industry.
Disclosure of Invention
The invention aims to provide a multispectral channel gas classification and quantitative detection method and a multispectral channel gas classification and quantitative detection system, so as to solve the problems in the background technology.
In order to achieve the above purpose, the present invention provides the following technical solutions:
a multi-spectral channel gas classification and quantitative detection method comprises the following steps:
Step 1, dividing an incident light beam into a plurality of sub-light beams through a multispectral light splitting module, and filtering to obtain N-1 sub-light beams with different narrowband spectrum bands and a broadband all-pass band sub-light beam;
step 2, converting the sub-beams of the N wave bands obtained in the step 1 into digital image signals of multi-band channels for simultaneous imaging through an infrared detector;
step 3, through an image distortion correction and registration unit, digital image signals which are simultaneously imaged by a multiband channel and are output by an infrared detector are subjected to distortion correction and are subjected to image registration alignment with images of different channels, and a spectrum image cube is output;
Step 4, carrying out pixel-level gas classification detection on the registered spectrum image cube output in the step 3 through a gas classification unit to obtain a pixel coordinate area and type information of gas distribution;
And 5, quantitatively solving a concentration equation of the pixel coordinate area and the type information of the gas distribution obtained in the step 4 through a gas quantitative unit, performing pseudo-color enhancement on the gas based on the gas concentration, and outputting the spatial distribution of the gas concentration.
Further, the step 1 specifically includes the following steps:
Step 1.1, an incident light beam is split into N sub-light beams through an aperture array module, wherein the aperture array module is a lens array formed by arranging N millimeter-level lenses;
Step 1.2, reserving one of N sub-beams, filtering the remaining N-1 sub-beams by using a filter array module to obtain N-1 sub-beams with different narrowband spectrum bands and a broadband all-pass band sub-beam, wherein the filter array module is a filter array formed by arranging N-1 narrowband band-pass filters with different center wavelengths.
Further, the step 3 specifically includes the following steps:
Step 3.1, cutting a digital image signal of simultaneous multi-band channel imaging into N sub-images, wherein the N sub-images comprise N-1 different narrowband spectrum band sub-images and one broadband all-pass band sub-image;
Step 3.2, registering the cut images by using an ORB algorithm;
And 3.3, arranging the registered multi-channel images into a spectrum image cube with N channels and outputting the spectrum image cube.
Further, the step 4 specifically includes the following steps:
step 4.1, introducing a normalized gas absorption spectrum database into a gas classification unit;
Step 4.2, calculating the registered spectrum image cube output in step 3 according to the following process:
The spectrum image cube is marked as I s, I s (x, y, c) represents a point with x-axis, y-axis and c-channel, the value of the point is a coordinate DN value, I s (x, y) represents a vector consisting of n DN values of I s(x,y,1)、Is(x,y,2)...Is (x, y, n), after the vector is normalized, the vector is classified by using a Bayesian optimization-based neural network, and the Bayesian optimization-based neural network outputs a gas type I to which each pixel point finally belongs and a probability p of an ith gas;
And 4.3, outputting pixel coordinate areas marked as gas distribution and type information.
The neural network further comprises a five-layer network structure, and comprises an input layer, three hidden layers and an output layer, wherein the number of neurons of the input layer is the number of spectrum channels, the number of neurons of the output layer is the number I of gas types needing to be classified, the Bayesian optimizer optimizes the super-parameters of the neural network based on initial values, the optimized super-parameters are as follows, the size of a first hidden layer is 71, the size of a second hidden layer is 164, regularization strength is 7.99425566291672e-06, an activation function is tanh, and a loss function is a cross entropy loss function.
Further, the step 5 specifically includes the following steps:
step 5.1, extracting DN values corresponding to all channel area points according to the pixel coordinate areas of the gas distribution output in the step 4;
And 5.2, carrying out difference on DN values of the gas pixels and DN values of surrounding background pixels to obtain delta DN (lambda), and selecting at least three narrow-band spectrum wavelength channels L a、Lb、Lc to obtain the following gas concentration equations respectively, and solving the inversion gas concentration by solving the following three equations:
Wherein e is a natural constant, λ a、λb、λc is the wavelength of the narrow-band spectral wavelength channel L a、Lb、Lc, τ s(λa)、τs(λb)、τs(λc) is the total band response of the narrow-band spectral wavelength channel L a、Lb、Lc, τ 2(λa)、τ2(λb)、τ2(λc) is the atmospheric transmittance of the wavelength λ a、λb、λc, which can be obtained by querying a Modtran radiation transmission model, K (λ a)、K(λb)、K(λc) is the absorption rate of the gas to be detected of the narrow-band spectral wavelength channel L a、Lb、Lc, which can be obtained by querying a Hitran database, ε (λ a)、ε(λb)、ε(λc) is the background emissivity of the narrow-band spectral wavelength channel L a、Lb、Lc, α (λ a)、α(λb)、α(λc) is the background emissivity of the narrow-band spectral wavelength channel L a、Lb、Lc, which is calculated by a planck formula of the wavelength λ a、λb、λc, β (λ a)、β(λb)、β(λc) is calculated by a planck formula of the wavelength λ a、λb、λc, and is the column density c·l of the gas, the background temperature T bg, the gas temperature T gas, which can be solved by substituting specific values into a ternary overrun equation after solving;
and 5.3, performing pseudo-color enhancement processing on the gas region of the broadband full-pass band subimage according to the concentration of the gas, and outputting the spatial distribution of the concentration of the gas.
The invention also provides a multispectral channel gas classification and quantitative detection system, which is used for realizing the multispectral channel gas classification and quantitative detection method, and comprises the following steps:
the multi-spectrum light splitting module is used for subdividing an incident light beam into sub-light beams with a plurality of wave bands;
The infrared detector is used for converting the sub-beams obtained by the multispectral light splitting module into digital image signals visible to naked eyes;
The gas classifying and quantifying module comprises an image distortion correcting and registering unit, a gas classifying unit and a gas quantifying unit, wherein the image distortion correcting and registering unit is used for correcting distortion of digital image signals output by an infrared detector and registering and aligning the digital image signals with images of different channels to output a multi-channel spectrum image cube, the gas classifying unit is used for classifying and detecting the gas of a pixel level of the registered spectrum image cube output by the image distortion correcting and registering unit to obtain pixel coordinate areas and type information of gas distribution, and the gas quantifying unit is used for quantitatively solving a concentration equation of the pixel coordinate areas and the type information of the gas distribution obtained by the output of the gas classifying unit, carrying out pseudo-color enhancement on the gas based on the gas concentration and outputting the spatial distribution of the gas concentration.
Further, the multispectral light splitting module comprises the following sub-modules:
the aperture array module is used for dividing an infrared incident beam into N sub-beams, and is a lens array formed by arranging N millimeter-level lenses;
the narrow-band bandpass filter array module is used for filtering the N-1 sub-beams to obtain N-1 sub-beams with different narrow-band spectrum bands, and the filter array module is a filter array formed by arranging N-1 narrow-band bandpass filters with different center wavelengths.
Compared with the prior art, the multi-spectral channel detection method has the advantages that the multi-spectral channel detection method can identify gas types and detect gas concentration compared with the traditional single-wavelength imaging detection method. The main innovation of multispectral channel detection is that by analyzing the absorption characteristics at different wavelengths, the presence of different gases can be distinguished more accurately. Even under the condition of overlapping absorption spectrums, the comprehensive utilization of multi-wavelength information can also obviously improve the identification accuracy. The redundant information of the multispectral channels enables the system to be more robust in the face of environmental noise and interference, and influences of non-target gases can be effectively filtered.
Through the innovations, the multispectral channel gas classification and quantitative detection method and the multispectral channel gas classification and quantitative detection system can remarkably improve the application level of the optical gas detection technology, and provide a more accurate and reliable solution for the fields of environmental monitoring, industrial control, public safety and the like.
Drawings
FIG. 1 is a flow chart of a multi-spectral channel gas classification and quantitative detection method of the present invention.
FIG. 2 is a schematic diagram of the operation of the gas classifying and quantifying module according to the present invention.
FIG. 3 is a schematic diagram of a multi-spectral channel gas classification and quantitative detection system according to the present invention.
Detailed Description
The following description of the embodiments of the present invention will be made clearly and completely with reference to the accompanying drawings, in which it is apparent that the embodiments described are only some embodiments of the present invention, but not all embodiments. All other embodiments, which can be made by those skilled in the art based on the embodiments of the invention without making any inventive effort, are intended to be within the scope of the invention.
Referring to fig. 1-2, a multi-spectral channel gas classification and quantitative detection method includes the following steps:
Step 1, dividing an incident light beam into a plurality of sub-light beams through a multispectral light splitting module, and filtering to obtain N-1 sub-light beams with different narrowband spectrum bands and a broadband all-pass band sub-light beam, wherein the method specifically comprises the following steps:
Step 1.1, an incident light beam is split into N sub-light beams through an aperture array module, wherein the aperture array module is a lens array formed by arranging N millimeter-sized lenses, and the N millimeter-sized lenses correspond to the N sub-light beams.
And 1.2, reserving one of N sub-beams, and filtering the remaining N-1 sub-beams by using a filter array module to obtain N-1 sub-beams with different narrowband spectrum bands and a broadband all-pass band sub-beam. The filter array module is a filter array formed by arranging N-1 narrow-band bandpass filters with different center wavelengths, and the rest N-1 sub-beams are filtered by the N-1 narrow-band bandpass filters with different center wavelengths in a one-to-one correspondence manner.
And 2, converting the sub-beams with the N wave bands obtained in the step 1 into digital image signals of multi-band channels for simultaneous imaging through an infrared detector.
Step 3, through the image distortion correction and registration unit, the digital image signals which are simultaneously imaged by the multiband channels and output by the infrared detector are subjected to distortion correction and are subjected to image registration alignment with images of different channels, and a spectrum image cube is output, and the method specifically comprises the following steps:
and 3.1, cutting the digital image signal of the multi-band channel simultaneous imaging into N sub-images, wherein the N sub-images comprise N-1 different narrow-band spectrum band sub-images and one broadband all-pass band sub-image.
Step 3.2, registering the cut images using ORB (Oriented FAST and Rotated BRIEF) algorithm.
And 3.3, arranging the registered multi-channel images into a spectrum image cube with N channels and outputting the spectrum image cube.
And 4, carrying out pixel-level gas classification detection on the registered spectrum image cube output in the step 3 through a gas classification unit to obtain a pixel coordinate area and type information of gas distribution, wherein the method specifically comprises the following steps of:
Step 4.1, introducing a normalized gas absorption spectrum database into the gas classification unit.
Step 4.2, calculating the registered spectrum image cube output in step 3 according to the following process:
The spectrum image cube is denoted as I s, I s (x, y, c) represents a point with x-axis, y-axis and c-channel, the value of which is a coordinate DN value, I s (x, y) represents a vector consisting of n DN values of I s(x,y,1)、Is(x,y,2)...Is (x, y, n), and after normalizing the vector, the vector is classified by using a Bayesian optimization-based neural network, and each pixel point is output to the gas class I and the probability p of the ith gas.
The neural network has a five-layer network structure and comprises an input layer, three hidden layers and an output layer, wherein the number of neurons of the input layer is the number of spectrum channels, the number of neurons of the output layer is the number I of gas types needing to be classified, the Bayesian optimizer optimizes the super-parameters of the neural network based on initial values, the optimized super-parameters are as follows, the size of a first hidden layer is 71, the size of a second hidden layer is 164, regularization intensity (lambda) is 7.99425566291672e-06, an activation function is tanh, and a loss function is a cross entropy loss function.
And 4.3, outputting pixel coordinate areas marked as gas distribution and type information, and outputting the result as shown in fig. 2.
And 5, quantitatively solving a concentration equation of the pixel coordinate area and the type information of the gas distribution obtained in the step 4 through a gas quantifying unit, performing pseudo-color enhancement on the gas based on the gas concentration, and outputting the spatial distribution of the gas concentration, wherein the method specifically comprises the following steps of:
and 5.1, extracting DN values corresponding to all channel area points according to the pixel coordinate areas of the gas distribution output in the step 4.
And 5.2, carrying out difference on DN values of the gas pixels and DN values of surrounding background pixels to obtain delta DN (lambda), and selecting at least three narrow-band spectrum wavelength channels L a、Lb、Lc to obtain the following gas concentration equations respectively, and solving the inversion gas concentration by solving the following three equations:
Wherein e is a natural constant, the value of which is about 2.718281828459045, λ a、λb、λc is the wavelength of the narrow-band spectral wavelength channel L a、Lb、Lc, τ s(λa)、τs(λb)、τs(λc) is the total band response of the narrow-band spectral wavelength channel L a、Lb、Lc, τ 2(λa)、τ2(λb)、τ2(λc) is the atmospheric transmittance of the wavelength λ a、λb、λc, which can be obtained by querying a Modtran radiation transmission model, K (λ a)、K(λb)、K(λc) is the absorption rate of the gas to be detected of the narrow-band spectral wavelength channel L a、Lb、Lc, which can be obtained by querying a Hitran database, ε (λ a)、ε(λb)、ε(λc) is the background emissivity of the narrow-band spectral wavelength channel L a、Lb、Lc, α (λ a)、α(λb)、α(λc) is the background emissivity of the narrow-band spectral wavelength channel L a、Lb、Lc, which is calculated by a planck formula of the wavelength λ a、λb、λc, β (λ a)、β(λb)、β(λc) is calculated by a planck formula of the wavelength λ a、λb、λc, and the unknown amounts are the column density c·l of the gas, the background temperature T bg, and the gas temperature T gas, and the column concentration, background temperature, of the gas and the gas temperature of the gas can be solved by introducing specific values into a solved ternary equation system.
And 5.3, performing pseudo-color enhancement processing on the gas region of the broadband full-pass band subimage according to the concentration of the gas, and outputting the spatial distribution of the concentration of the gas.
Referring to fig. 3, a multi-spectral channel gas classification and quantitative detection system is used for implementing the multi-spectral channel gas classification and quantitative detection method as described above, and includes a multi-spectral light-splitting module, an infrared detector, and a gas classification and quantitative module.
The multi-spectrum light splitting module is used for subdividing an incident light beam into sub-beams with a plurality of wave bands and comprises an aperture array module and a narrow-band pass filter array module, wherein the aperture array module is used for dividing an infrared incident light beam into N sub-beams, and the narrow-band pass filter array module is used for filtering N-1 sub-beams to obtain N-1 sub-beams with different narrow-band spectrum wave bands and a broadband all-pass wave band sub-beam. The aperture array module is a lens array formed by arranging N millimeter-sized lenses. The filter array module is an optical filter array formed by arranging N-1 narrow-band bandpass filters with different center wavelengths.
The infrared detector is used for converting the sub-beams obtained by the multispectral light splitting module into digital image signals visible to naked eyes.
The gas classifying and quantifying module is a computer program, is stored and operated in an upper computer, and comprises an image distortion correcting and registering unit, a gas classifying unit and a gas quantifying unit.
The image distortion correction and registration unit is used for correcting distortion of the digital image signal output by the infrared detector and performing image registration alignment with images of different channels, and outputs a spectrum image cube, and the image distortion correction and registration unit is a computer program, and specific implementation of the image distortion correction and registration unit can be seen in the step 3 and is not repeated here.
The gas classification unit is used for classifying and detecting the gas at the pixel level on the spectrum image cube after the registration output by the image distortion correction and registration unit, so as to obtain the pixel coordinate area and the kind information of the gas distribution, and the gas classification unit is a computer program, and the specific implementation of the gas classification unit can be seen in the step 4 and is not repeated here.
The gas quantifying unit is used for quantitatively solving a concentration equation of the pixel coordinate area and the type information of the gas distribution obtained by the output of the gas classifying unit, performing pseudo-color enhancement on the gas based on the gas concentration, and outputting the spatial distribution of the gas concentration, and the specific implementation of the gas quantifying unit is a computer program, and can be seen in the step 5 and is not repeated herein.
Although embodiments of the present invention have been shown and described, it will be understood by those skilled in the art that various changes, modifications, substitutions and alterations can be made therein without departing from the principles and spirit of the invention, the scope of which is defined in the appended claims and their equivalents.
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