Photoelectric gas monitoring device and method

By enhancing the optical signal through Tesla coil ionization and nonlinear optical effects, the sensitivity and multi-gas adaptability issues of trace gas detection in photoelectric gas monitoring technology are solved, and efficient and accurate gas concentration calculation and report generation are achieved.

CN119959168BActive Publication Date: 2025-09-12JIUXINGLONG ENG TECH WUXI CO LTD
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Patent Information

Application Number
CN202510072075.9
Authority / Receiving Office
CN · China
Patent Type
Patents(China)
Current Assignee / Owner
Filing Date
2025-01-17
Publication Date
2025-09-12
Estimated Expiration
2045-01-17

AI Technical Summary

Technical Problem

Existing photoelectric gas monitoring technology lacks sensitivity in trace gas detection and adaptability in multi-gas detection. Traditional methods are difficult to provide sufficient signal strength and accuracy in complex environments.

Method used

Tesla coils are used for gas ionization, and nonlinear optical effects are combined to enhance light signals. Spectral separation and photoelectric conversion are used to calculate gas concentrations and generate detection reports.

Benefits of technology

It achieves high-sensitivity and high-adaptability trace gas monitoring, can accurately detect multiple gases in complex environments, and improves signal strength and detection accuracy.

✦ Generated by Eureka AI based on patent content.

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Abstract

The present invention discloses a photoelectric gas monitoring device and method, which relates to the field of photoelectric detection technology, including ionizing a pre-treated target gas through a Tesla coil to generate a light signal; optically detecting the light signal through spectral separation and light signal detection; nonlinearly enhancing the light signal through a nonlinear optical effect and converting it into an electrical signal; calculating the actual concentration of the gas based on the electrical signal and generating a detection report. By performing ionization and nonlinear optical effect enhancement through a Tesla coil, a highly sensitive and highly adaptable photoelectric gas monitoring method is achieved. Among them, the Tesla coil ionization step solves the problems of insufficient light signal intensity and poor multi-gas adaptability, while the nonlinear optical effect enhancement step significantly improves detection sensitivity and signal quality. The present invention can achieve efficient monitoring of trace gases in complex environments, providing a new technical means for environmental protection, industrial safety and medical diagnosis.
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Description

Technical Field

[0001] The present invention relates to the field of photoelectric detection technology, and in particular to a photoelectric gas monitoring device and method. Background Art

[0002] Photoelectric gas monitoring, a core technology in modern environmental monitoring, industrial safety, medical diagnostics, and scientific research, has achieved significant progress in recent years. Traditional gas monitoring methods, including chemical sensors, thermal conductivity detection, and low-resolution spectrometers, have demonstrated limited applicability in specific application scenarios. However, these methods suffer from limited sensitivity and detection accuracy, particularly in trace gas monitoring. With advances in laser technology, spectral detection, and photoelectric conversion technologies, high-sensitivity photoelectric gas monitoring methods have become a research hotspot. Photoelectric gas monitoring utilizes specific interactions between light and gas molecules (such as absorption, scattering, or fluorescence) combined with photoelectric conversion devices to enable non-contact detection of gas composition and concentration. In recent years, the introduction of high-reflectivity optical cavities and nonlinear optical effects has significantly improved detection sensitivity. Tesla coils, due to their ability to generate high-frequency electromagnetic fields and effectively ionize gases, have been applied in various fields. However, while the development of individual technologies has improved the performance of photoelectric gas monitoring, these technologies still face numerous limitations in practical applications.

[0003] The shortcomings of existing photoelectric gas monitoring technologies are primarily reflected in the following two aspects: First, existing technologies have limitations in terms of sensitivity for trace gas detection. Traditional optical detection methods are limited by the intensity of the optical signal itself, and it is difficult to provide sufficient signal strength for detecting low-concentration gases (ppb level or even lower). Although high-reflectivity optical cavities can enhance optical signals by extending the optical path, this approach has limited noise suppression capabilities and, in complex mixed gas environments, can interfere with signal accuracy. Second, current gas monitoring solutions lack adaptability in terms of detection range. Most existing monitoring systems are optimized only for the detection of specific gases and cannot effectively cover the multiple gases in complex environments, limiting their application in multi-gas mixtures. In addition, some technologies rely on gas concentration to enhance the detection signal, but this process may change the original composition or concentration of the gas, increasing errors and reducing the applicability of the system. In summary, existing photoelectric gas monitoring technologies still have considerable room for improvement in terms of sensitivity and multi-gas detection capabilities. Summary of the Invention

[0004] In view of the above existing problems, the present invention is proposed.

[0005] Therefore, the present invention provides a photoelectric gas monitoring method to solve the problems of insufficient trace gas detection sensitivity and high system complexity.

[0006] In order to solve the above technical problems, the present invention provides the following technical solutions:

[0007] In a first aspect, the present invention provides a photoelectric gas monitoring method, which includes collecting target gas through a sampling pump and pre-processing the collected target gas; ionizing the pre-treated target gas through a Tesla coil to generate a light signal; optically detecting the light signal through spectral separation and light signal detection; nonlinearly enhancing the light signal through nonlinear optical effects and converting it into an electrical signal; calculating the actual concentration of the gas based on the electrical signal and generating a detection report.

[0008] As a preferred embodiment of the photoelectric gas monitoring method of the present invention, the target gas is collected by a sampling pump and the collected target gas is pre-processed. The specific steps are as follows:

[0009] The original target gas enters the sampling pipeline through the sampling pump, and the target gas is collected through the sampling pipeline. The collected target gas is filtered for particles, regulated for humidity, regulated for temperature and pressure, and tested for quality.

[0010] As a preferred embodiment of the photoelectric gas monitoring method of the present invention, the pre-treated target gas is ionized by the Tesla coil to generate a light signal. The specific steps are as follows:

[0011] Through the oscillation of the inductor coil of the Tesla coil and the capacitor, a high-frequency electromagnetic field is generated, which excites the pre-treated target gas into a plasma state and releases a light signal.

[0012] As a preferred embodiment of the photoelectric gas monitoring method of the present invention, the optical signal is optically detected by spectral separation and optical signal detection, and the specific steps are as follows:

[0013] Through spectral separation and light signal detection, the absorption intensity of the light signal is calculated, and the expression is:

[0014]

[0015] Where I is the intensity of the detected light signal, I0 is the intensity of the incident light, and α i is the absorption coefficient of the i-th gas, C i is the concentration of the i-th gas, L is the physical length of the optical cavity, and R is the reflectivity of the mirror.

[0016] As a preferred solution of the photoelectric gas monitoring method of the present invention, wherein: the nonlinear enhancement of the optical signal by the nonlinear optical effect is performed, the specific steps are as follows:

[0017] The optical signal is passed through the second harmonic crystal for nonlinear interaction to generate frequency-doubled light. The intensity of the frequency-doubled light is calculated as follows:

[0018]

[0019] Among them, I SHG is the intensity of the doubled frequency light, η is the nonlinear efficiency coefficient, d eff is the nonlinear efficiency coefficient, ∈0 is the vacuum permittivity, λ is the wavelength of the input light, n1 is the refractive index of the input light, n2 is the refractive index of the doubled frequency light, c is the speed of light in vacuum, represents the influence factor of wave vector matching, and D is the physical length of the crystal.

[0020] As a preferred embodiment of the photoelectric gas monitoring method of the present invention, the conversion into an electrical signal is carried out in the following specific steps:

[0021] The frequency-doubled light is received by a highly sensitive photodetector and converted into an electrical signal. The photodetector outputs a current expressed as:

[0022] I e =p·I SHG ;

[0023] Among them, I e is the photocurrent output by the detector, and p is the photoresponsivity of the photodetector.

[0024] As a preferred embodiment of the photoelectric gas monitoring method of the present invention, the actual concentration of the gas is calculated based on the electrical signal and a detection report is generated. The specific steps are as follows:

[0025] The received electrical signal is calibrated and normalized by using a cavity without gas and a cavity with a known concentration of gas. Based on the normalized electrical signal, the actual ambient concentration of the gas is calculated using the expression:

[0026]

[0027] Among them, C env,i is the actual environmental concentration of the i-th gas, I n,i is the normalized electrical signal intensity, β i is the gas absorption coefficient, L is the optical path length;

[0028] The actual environmental concentration of the target gas, detection time, environmental parameters and equipment status are integrated to generate a detection report.

[0029] In second aspect, the present invention provides a photoelectric gas monitoring system, including a sampling and preprocessing module, which is used to collect target gas through a sampling pump and preprocess the collected target gas; an ionization module, which is used to ionize the pretreated target gas through a Tesla coil to generate a light signal; an optical detection module, which is used to optically detect the light signal through spectral separation and light signal detection; a nonlinear enhancement module, which is used to nonlinearly enhance the light signal through nonlinear optical effects and convert it into an electrical signal; and a detection report module, which is used to calculate the actual concentration of the gas based on the electrical signal and generate a detection report.

[0030] In a third aspect, the present invention provides a computer device comprising a memory and a processor, wherein the memory stores a computer program, wherein: when the computer program is executed by the processor, any step of the photoelectric gas monitoring method as described in the first aspect of the present invention is implemented.

[0031] In a fourth aspect, the present invention provides a computer-readable storage medium having a computer program stored thereon, wherein: when the computer program is executed by a processor, any step of the photoelectric gas monitoring method as described in the first aspect of the present invention is implemented.

[0032] The present invention achieves a highly sensitive and adaptable photoelectric gas monitoring method through ionization and nonlinear optical effect enhancement using a Tesla coil. The Tesla coil ionization step addresses issues such as insufficient optical signal intensity and poor multi-gas adaptability, while the nonlinear optical effect enhancement step significantly improves detection sensitivity and signal quality. The combination of these innovative technologies enables efficient trace gas monitoring in complex environments, providing new technical solutions for environmental protection, industrial safety, and medical diagnosis. BRIEF DESCRIPTION OF THE DRAWINGS

[0033] In order to more clearly illustrate the technical solutions of the embodiments of the present invention, the following briefly introduces the drawings required for use in the description of the embodiments. Obviously, the drawings described below are only some embodiments of the present invention. For ordinary technicians in this field, other drawings can be obtained based on these drawings without paying any creative work.

[0034] Figure 1 Flowchart of the photoelectric gas monitoring method in Example 1.

[0035] Figure 2 Schematic diagram of the photoelectric gas monitoring system in Example 1. DETAILED DESCRIPTION

[0036] In order to make the above-mentioned objects, features and advantages of the present invention more obvious and easy to understand, the specific embodiments of the present invention are described in detail below with reference to the accompanying drawings.

[0037] In the following description, many specific details are set forth to facilitate a full understanding of the present invention. However, the present invention may also be implemented in other ways different from those described herein. Those skilled in the art may make similar generalizations without violating the connotation of the present invention. Therefore, the present invention is not limited to the specific embodiments disclosed below.

[0038] Secondly, the term "one embodiment" or "embodiment" herein refers to a specific feature, structure, or characteristic that may be included in at least one implementation of the present invention. The phrase "in one embodiment" appearing in various places throughout this specification does not necessarily refer to the same embodiment, nor does it refer to a separate or selective embodiment that is mutually exclusive of other embodiments.

[0039] Example 1, reference Figure 1 and Figure 2 , which is the first embodiment of the present invention, provides a photoelectric gas monitoring method, comprising the following steps:

[0040] S1: Collect target gas through a sampling pump and pre-treat the collected target gas;

[0041] Furthermore, the original target gas enters the sampling pipeline through the sampling pump, the target gas is collected through the sampling pipeline, and the collected target gas is subjected to particle filtering, humidity adjustment, temperature and pressure adjustment, and quality inspection.

[0042] It should be noted that suspended particulate matter in the gas is intercepted by a particulate filter, water vapor is condensed into liquid water and separated from the air flow by a condensation and dehumidification device, pressure is adjusted by a pressure control valve, temperature is adjusted by a thermostat, and quality is detected by a gas quality sensor.

[0043] S2: Ionize the pre-treated target gas through the Tesla coil to generate a light signal;

[0044] Furthermore, through the oscillation of the inductor coil of the Tesla coil and the capacitor, a high-frequency electromagnetic field is generated, which excites the pre-treated target gas into a plasma state and releases a light signal.

[0045] It should be noted that gas molecules are excited to a high-energy state by the electromagnetic field, and when the high-energy state molecules return to the ground state, they release light signals of a specific wavelength.

[0046] S3: optically detecting the light signal through spectral separation and light signal detection;

[0047] Furthermore, the absorption intensity of the light signal is calculated through spectral separation and light signal detection, and the expression is:

[0048]

[0049] Where I is the intensity of the detected light signal, I0 is the intensity of the incident light, and α i is the absorption coefficient of the i-th gas, C i is the concentration of the i-th gas, L is the physical length of the optical cavity, and R is the reflectivity of the mirror.

[0050] It should be noted that the light signal released by the ionized gas passes through a spectral filter to separate the target spectral band, and a broadband light source (ultraviolet-visible light or infrared light) is used to interact with the gas molecules to supplement the spectral information; after the light signal is separated by the spectral filter, it directly enters the subsequent nonlinear optical enhancement module.

[0051] S4: Nonlinear enhancement of optical signals through nonlinear optical effects and conversion into electrical signals;

[0052] Furthermore, the optical signal is passed through the second harmonic crystal for nonlinear interaction to generate frequency-doubled light. The intensity of the frequency-doubled light is calculated as follows:

[0053]

[0054] Among them, I SHG is the intensity of the doubled frequency light, η is the nonlinear efficiency coefficient, d eff is the nonlinear efficiency coefficient, ∈0 is the vacuum permittivity, λ is the wavelength of the input light, n1 is the refractive index of the input light, n2 is the refractive index of the doubled frequency light, c is the speed of light in vacuum, represents the influence factor of wave vector matching, and D is the physical length of the crystal;

[0055] It should be noted that the intensity of the frequency-doubled light I SHG ≥0, when the input light intensity I=0 or the wave vector mismatch is serious, the frequency doubled signal is 0. When the input light intensity increases or the wave vector is well matched, the frequency doubled signal reaches the maximum value. The value range is [0, 1], indicating the efficiency of wave-vector matching. When the value is 1, the matching is optimal. The optical signal undergoes nonlinear interaction through the second harmonic crystal, generating frequency-doubled light. The intensity of the frequency-doubled light depends on the nonlinear efficiency coefficient of the crystal, the vacuum permittivity, the wavelength and refractive index of the input light, the refractive index of the frequency-doubled light, the speed of light in vacuum, the wave-vector matching factor, and the physical length of the crystal. The intensity of the frequency-doubled light is calculated through a comprehensive formula, enabling the description and analysis of nonlinear optical processes.

[0056] The frequency-doubled light is received by a highly sensitive photodetector and converted into an electrical signal. The photodetector outputs a current expressed as:

[0057] I e =p·I SHG ;

[0058] Among them, I e is the photocurrent output by the detector, and p is the photoresponsivity of the photodetector.

[0059] It should be noted that I e ≥0, when the frequency-doubled light intensity is zero, the detector output current is zero; the higher the frequency-doubled light intensity, the greater the detector output current, R p A typical value is about 0.4.

[0060] S5: Calculate the actual concentration of the gas based on the electrical signal and generate a detection report.

[0061] Furthermore, the received electrical signal is calibrated and normalized by using a cavity without gas and a gas with a known concentration. Based on the normalized electrical signal, the actual ambient concentration of the gas is calculated using the expression:

[0062]

[0063] Among them, C env,i is the actual environmental concentration of the i-th gas, I n,i is the normalized electrical signal intensity, β i is the gas absorption coefficient, L is the optical path length;

[0064] Integrate the actual environmental concentration of the target gas, detection time, environmental parameters and equipment status to generate a detection report;

[0065] It should be noted that the calculated C env,i is the actual ambient concentration of the i-th gas, which is normalized and corrected according to the ambient temperature and pressure;

[0066] The actual environmental concentration of the target gas, detection time, environmental parameters and equipment status are integrated to generate a detection report.

[0067] It should be noted that the gas concentration is the final corrected standard concentration, the detection time is the specific detection time and date, accurate to seconds, the environmental parameters include actual detection conditions such as temperature, pressure, and humidity, and the equipment status includes equipment operating parameters such as laser power, detector gain, and optical cavity reflectivity.

[0068] This embodiment also provides a photoelectric gas monitoring system, including: a sampling and preprocessing module, which is used to collect target gas through a sampling pump and preprocess the collected target gas; a gas concentration module, which is used to concentrate the pretreated gas to generate concentrated high-purity target gas; an optical detection module, which is used to form an optical signal based on the concentrated high-purity target gas by absorbing light energy through an optical cavity; a nonlinear enhancement module, which is used to nonlinearly enhance the optical signal through a nonlinear optical effect and convert it into an electrical signal; and a detection report module, which is used to calculate the concentration of the target gas based on the electrical signal and generate a detection report.

[0069] This embodiment also provides a computer device suitable for the photoelectric gas monitoring method, including: a memory and a processor; the memory is used to store computer-executable instructions, and the processor is used to execute computer-executable instructions to implement the photoelectric gas monitoring method proposed in the above embodiment.

[0070] The computer device may be a terminal, comprising a processor, a memory, a communication interface, a display screen and an input device connected via a system bus. The processor of the computer device is used to provide computing and control capabilities. The memory of the computer device comprises a non-volatile storage medium and an internal memory. The non-volatile storage medium stores an operating system and a computer program. The internal memory provides an environment for the operation of the operating system and the computer program in the non-volatile storage medium. The communication interface of the computer device is used to communicate with an external terminal in a wired or wireless manner, and the wireless manner may be achieved through WIFI, an operator network, NFC (near field communication) or other technologies. The display screen of the computer device may be a liquid crystal display or an electronic ink display screen, and the input device of the computer device may be a touch layer covering the display screen, or a button, trackball or touchpad provided on the housing of the computer device, or an external keyboard, touchpad or mouse.

[0071] This embodiment also provides a storage medium having a computer program stored thereon, which, when executed by a processor, implements the photoelectric gas monitoring method proposed in the above embodiment; the storage medium can be implemented by any type of volatile or non-volatile storage device or a combination thereof, such as static random access memory (SRAM), electrically erasable programmable read-only memory (EEPROM), erasable programmable read-only memory (EPROM), programmable read-only memory (PROM), read-only memory (ROM), magnetic memory, flash memory, disk or optical disk.

[0072] In summary, the present invention achieves a highly sensitive and adaptable photoelectric gas monitoring method through Tesla coil ionization and nonlinear optical effect enhancement. The Tesla coil ionization step addresses the issues of insufficient optical signal intensity and poor multi-gas adaptability, while the nonlinear optical effect enhancement step significantly improves detection sensitivity and signal quality. The combination of these innovative technologies enables efficient trace gas monitoring in complex environments, providing new technical solutions for environmental protection, industrial safety, and medical diagnosis.

[0073] It should be noted that the above embodiments are only used to illustrate the technical solutions of the present invention and are not intended to limit the present invention. Although the present invention has been described in detail with reference to the preferred embodiments, those skilled in the art should understand that the technical solutions of the present invention may be modified or replaced by equivalents without departing from the spirit and scope of the technical solutions of the present invention, which should all be included in the scope of the claims of the present invention.

Claims

1. A photoelectric gas monitoring method, characterized in that: include, Collect target gas through a sampling pump and pre-treat the collected target gas; The pre-treated target gas is ionized by a Tesla coil to generate a light signal; Through spectrum separation and optical signal detection, the optical signal is optically detected. The specific steps are as follows: Through spectral separation and light signal detection, the absorption intensity of the light signal is calculated, and the expression is: Where I is the intensity of the detected light signal, I0 is the intensity of the incident light, and α i is the absorption coefficient of the i-th gas, C i is the concentration of the i-th gas, L is the physical length of the optical cavity, and R is the reflectivity of the mirror; The optical signal is nonlinearly enhanced through nonlinear optical effects and converted into an electrical signal. The specific steps are as follows: The optical signal is passed through the second harmonic crystal for nonlinear interaction to generate frequency-doubled light. The intensity of the frequency-doubled light is calculated as follows: Among them, I SHG is the intensity of the doubled frequency light, η is the nonlinear efficiency coefficient, d eff is the nonlinear efficiency coefficient, 0 is the vacuum permittivity, λ is the wavelength of the input light, n1 is the refractive index of the input light, n2 is the refractive index of the doubled frequency light, c is the speed of light in vacuum, represents the influence factor of wave vector matching, and D is the physical length of the crystal; The actual concentration of the gas is calculated based on the electrical signal and a detection report is generated.

2. The photoelectric gas monitoring method according to claim 1, wherein: The target gas is collected by a sampling pump and pre-processed. The specific steps are as follows: The original target gas enters the sampling pipeline through the sampling pump, and the target gas is collected through the sampling pipeline. The collected target gas is filtered for particles, regulated for humidity, regulated for temperature and pressure, and tested for quality.

3. The photoelectric gas monitoring method according to claim 2, wherein: The Tesla coil is used to ionize the pre-treated target gas to generate a light signal. The specific steps are as follows: Through the oscillation of the inductor coil of the Tesla coil and the capacitor, a high-frequency electromagnetic field is generated, which excites the pre-treated target gas into a plasma state and releases a light signal.

4. The photoelectric gas monitoring method according to claim 1, wherein: The conversion into electrical signals is carried out in the following specific steps: The frequency-doubled light is received by a highly sensitive photodetector and converted into an electrical signal. The photodetector outputs a current expressed as: I e =p·I SHG ; Among them, I e is the photocurrent output by the detector, and p is the photoresponsivity of the photodetector.

5. The photoelectric gas monitoring method according to claim 4, wherein: The actual concentration of the gas is calculated based on the electrical signal and a detection report is generated. The specific steps are as follows: The received electrical signal is calibrated and normalized by using a cavity without gas and a cavity with a known concentration of gas. Based on the normalized electrical signal, the actual ambient concentration of the gas is calculated using the expression: Among them, C env,i is the actual environmental concentration of the i-th gas, I n,i is the normalized electrical signal intensity, β i is the gas absorption coefficient, L is the optical path length; The actual environmental concentration of the target gas, detection time, environmental parameters and equipment status are integrated to generate a detection report.

6. A photoelectric gas monitoring system based on the photoelectric gas monitoring method according to any one of claims 1 to 5, characterized in that: Including sampling and pre-processing module, gas concentration module, optical detection module, nonlinear enhancement module and detection report module, The sampling and pre-processing module is used to collect the target gas through the sampling pump and pre-process the collected target gas; An ionization module, used to ionize the pre-treated target gas through a Tesla coil to generate a light signal; an optical detection module, for optically detecting the optical signal through spectral separation and optical signal detection; A nonlinear enhancement module, used to perform nonlinear enhancement on the optical signal through nonlinear optical effects and convert it into an electrical signal; The detection report module is used to calculate the actual concentration of the gas based on the electrical signal and generate a detection report.

7. A computer device comprising a memory and a processor, wherein the memory stores a computer program, wherein: When the processor executes the computer program, the steps of the photoelectric gas monitoring method according to any one of claims 1 to 5 are implemented.

8. A computer-readable storage medium having a computer program stored thereon, characterized in that: When the computer program is executed by a processor, the steps of the photoelectric gas monitoring method according to any one of claims 1 to 5 are implemented.

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