Laser gas analyzer. Laser optical-acoustic gas analyzer of intracavity type. Functionality of the complex

Characteristic

The device is designed for operational gas analysis of atmospheric air by the method of optical-acoustic laser spectroscopy

The principle of operation of the gas analyzer is based on the generation of acoustic waves in air when a modulated laser beam interacts with molecules of a gas impurity that absorbs laser radiation at a given wavelength. Acoustic waves are converted by the microphone into electrical signals proportional to the concentration of the absorbing gas. By tuning the laser wavelength and using the known spectral data on the absorption coefficients of various gases, it is possible to determine the composition of the detected gas impurity.

A distinctive feature of this gas analyzer is the combination in a single design of a tunable waveguide CO2 laser and a pumped optical-acoustic detector (OAD) of a differential type. The OAD is located inside the laser cavity and forms a single structure with the laser. Due to this, the losses on the optical elements are reduced, the power inside the working channel of the OAD and the rigidity of the entire structure increase. The gas analyzer uses an automatically line-tuned waveguide CO2 laser with high-frequency (HF) excitation, in which a repetitively pulsed generation mode is set by modulating the power of the RF generator, which makes it possible to optimize power consumption by adjusting the duty cycle of the excitation pulses. In the design of the used differential type OAD, there are two resonant acoustic channels, in

which form antiphase acoustic waves, which makes it possible, with the introduction of appropriate treatment, to minimize noise when air flows through the channels.

These features of the device are unique and together provide an extremely high detection sensitivity for optical-acoustic devices, a low level of hardware noise and a relatively low total power consumption.

The gas analyzer is capable of registering the minimum absorption coefficients of gaseous impurities in the atmosphere in a gas flow at a level of ~ 5 × 10-10 cm-1 with a high response rate inherent in optical methods of gas analysis. Due to these qualities, as well as the possibility of tuning the wavelength of laser radiation in the range of 9.3 ÷ 10.9 μm, the gas analyzer allows real-time measurements of low concentrations of atmospheric and anthropogenic gases (at a level of 1 ppb or less), such as C2

Н4, NH3, O3, C6, SO2, SF6, N2

O, CH3, CH3, etc.,

including a series of vapors of explosive and toxic substances (about 100 substances in total).

These properties make it possible to use the device for monitoring the concentration of chemical molecular compounds in the atmospheric air and technological processes, analyze the exhaled air in order to detect various diseases, etc.

Applying an effect

The obvious advantages of the OA method in combination with the use of sufficiently powerful cw frequency-tunable lasers make it especially attractive for solving problems requiring measurements of weak absorption of radiation by molecular gases. First of all, this concerns the problems of gas analysis at low and ultra-low concentrations of molecules in the medium.

Topic article

Parametric synthesis of the base station antenna according to the specified requirements for the radiation pattern
An antenna is a radio technical device designed to study or receive electromagnetic waves. The antenna is one of the most important elements of any radio engineering system associated with the emission or reception of radio waves. Such systems include: radio communication systems, ra ...


Holders of the patent RU 2613200:

The invention relates to the field of measuring technology and can be used for qualitative and quantitative analysis of gaseous media.

Among the various methods of gas analysis, a special place is occupied by the method based on Raman spectroscopy (RS) of light. The Raman spectra are explained by the scattering of exciting laser radiation by molecules at frequencies corresponding to their internal structure, and the intensity of these spectra depends linearly on the number of molecules. Thus, the essence of this method lies in the registration of Raman spectra and carrying out a qualitative and quantitative analysis of gaseous media using them. First of all, this approach is distinguished by the absence supplies and complex sample preparation, high speed, as well as the possibility of simultaneous control of all molecular compounds of the analyzed gas medium, the content of which exceeds the sensitivity threshold of the equipment. Due to these advantages, this type of gas analyzers is one of the most promising today.

It should be noted that the main disadvantage of gas analysis using Raman spectroscopy is the low intensity of informative signals, which is directly reflected in the values \u200b\u200bof the threshold limits for the detection of gas components and the relatively low reliability of the gas analysis.

Known laser analyzer, based on the method of spectroscopy of Raman light scattering [certificate of useful model No. 10462, 1999, G01N21 / 25]. Despite the fact that this device is intended for gas analysis of natural gas, it is capable of diagnosing other gas environments. This analyzer contains a laser, a focusing lens, a gas cuvette, a condenser lens, a depolarizing wedge, a holographic filter, a polychromator containing a concave diffraction grating, a receiving unit containing a distribution element and photodiode arrays, as well as a control unit and a computer. The essence of his work consists in registering the spectrum of Raman scattering of light of the investigated gaseous medium and carrying out qualitative and quantitative analysis on it. The main disadvantage this device is the low reliability of the analysis due to the low intensity of the recorded Raman spectra. This circumstance, in turn, is due to the use of a lens for collecting scattered light with a low aperture ratio (1: 6) and the specificity of a polychromator using a concave diffraction grating and, accordingly, also having a low aperture ratio.

The closest in principle of operation (prototype) is a natural gas composition analyzer [RF Patent No. 126136, 2013, G01N 21/00]. This analyzer is also based on Raman spectroscopy and has the potential to analyze any molecular compound. This analyzer is partially free from the disadvantage of the device described above in terms of the use of components with low aperture ratio. The specified device includes a laser, a focusing lens, a gas cuvette, a photographic lens with an aperture ratio of 1: 1.8, a holographic filter, a control unit, and a high-aperture spectral device with a flat diffraction grating, coupled with a CCD matrix.

Nevertheless, the main disadvantage of this gas analyzer is the low reliability of the analysis due to the relatively low intensity of the recorded Raman spectra.

The problem to be solved by the invention is to increase the intensity of the recorded Raman spectra by increasing the density of molecules in the region of interaction of the laser beam and the analyzed gas.

The technical result is to increase the reliability of the gas analysis.

This result is achieved by the fact that in a system containing a continuous laser, a focusing lens, a gas cell with an input window for inputting laser radiation and a window for outputting scattered radiation at an angle of 90 °, a photo lens, a holographic filter that attenuates the scattered radiation at the laser wavelength, a spectral device coupled to a CCD matrix and a control unit, unlike the prototype, the internal faces of the gas cell are made in such a way that they form a rectangular parallelepiped, and on the face that does not have a window and is parallel to another face that also does not have a window an acoustic emitter with a frequency that creates a standing sound wave inside the cuvette perpendicular to the laser beam and provides a gas compression region in the focusing area.

It is known that an acoustic wave is an alternating area of \u200b\u200bcompression and rarefaction of the medium in which it propagates. The execution of the inner edges of the cuvette in such a way that a rectangular parallelepiped is formed, as well as the provision of conditions for the formation of a standing wave inside it (see relation 1) allows these regions to be fixed in space, and due to resonance, the pressure difference in them will increase.

where l is the propagation length of the acoustic wave, λ is the wavelength, n is an odd integer (1, 3, 5, ...), since the laser beam passes through the center of the cuvette.

Thus, in the focusing region of the laser beam inside the cuvette, a gas compression region is provided, characterized by an increase in the density of molecules and, accordingly, their concentration, which provides an increase in the intensity of Raman signals due to relation 2.

I \u003d I 0 NΩσ, (2)

where I is the intensity of the Raman signals, I 0 is the intensity of the exciting laser radiation, Ω is the collection angle of scattered radiation, N is the concentration of molecules of a given type, σ is the scattering cross section.

In turn, an increase in the intensity of informative RR signals is guaranteed to lead to an increase in the reliability of the gas analysis.

FIG. 1 shows a block diagram of the proposed laser gas analyzer (side view).

FIG. 2 shows a block diagram of the gas analyzer (top view).

Laser gas analyzer contains a laser (1) operating in a continuous mode, a focusing lens (2), a gas cell (3) equipped with a window for laser radiation input (4) and a window for scattered light output (5), an acoustic emitter (6), a photo lens ( 7) for collecting scattered radiation, a holographic filter (8), a spectral device (9), a CCD matrix (10) and a control unit (11).

The proposed laser gas analyzer operates as follows. The exciting radiation from the laser 1 is focused by the lens 2 in the center of the gas cell 3, passing through the entrance window 4. An acoustic emitter 6 is installed inside the cell 3, generating acoustic waves. Due to its location from the opposite edge of the cuvette at a distance that is a multiple of half the acoustic wavelength, a standing acoustic wave is formed inside the cuvette with a compression region in the focusing region of the laser beam. The laser radiation, in turn, is scattered by the molecules of the analyzed gas inside the cuvette. This scattered radiation, the highest power density of which is in the center of the cuvette, exits through the window 5 and is collected by the photo lens 7. This lens directs the collected radiation to the entrance slit of the spectral device 9, through the holographic filter 8, the role of which is to weaken the intensity of elastic light scattering at the frequency of the exciting radiation ... The spectral device 9 decomposes the light that has entered it into a spectrum, which is then recorded by the CCD matrix 10. The latter transmits electrical signals to the control unit 11, where they can be processed and stored.

The direct calculation of the qualitative and quantitative composition of the analyzed gaseous medium from the recorded Raman spectrum can be carried out either in the control unit or transferred from it to a computer.

The proposed invention is characterized by a higher reliability of the analysis due to the registration of the Raman spectra of gases with a higher intensity and, accordingly, a higher signal-to-noise ratio.

Laser gas analyzer containing a continuous laser, a focusing lens, a gas cell with an entrance window for laser radiation input and a window for scattered radiation output at an angle of 90 °, a photo lens, a holographic filter that attenuates the scattered radiation at the laser wavelength, a spectral device coupled to a CCD -matrix, and a control unit, characterized in that the inner edges of the gas cell are made in such a way that they form a rectangular parallelepiped, and on the edge that does not have a window and is parallel to another edge that also does not have a window, an acoustic emitter is installed with a frequency that creates inside cuvette standing sound wave perpendicular to the laser beam and providing a gas compression region in the focusing area.

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The invention relates to the field of optical sensors that register molecular groups and operate in the visible frequency range. The renewable substrate for detecting surface-enhanced Raman scattering consists of a nanostructured SERS substrate and a passivating dielectric layer.

The invention relates to measuring equipment and can be used for qualitative and quantitative analysis of gaseous media. The laser gas analyzer contains a continuous laser, a focusing lens, a gas cell with an entrance window for laser radiation input and a window for scattered radiation output at an angle of 90 °, a photo lens, a holographic filter, a spectral device coupled to a CCD matrix, and a control unit. The inner faces of the gas cuvette form a rectangular parallelepiped, and on the face that does not have a window and is parallel to another face that also does not have a window, an acoustic emitter is installed, which creates a standing sound wave inside the cuvette perpendicular to the laser beam and provides a gas compression region in the focusing region. The technical result of the invention is to improve the reliability of the gas analysis. 2 ill.

Laser gas analyzer "LGAU-02" is designed to measure the concentration of gaseous hydrocarbons in the air pumped through the gas cell of the device. The gas analyzer can be used both in a stand-alone version and as part of mobile auto and air laboratories. The complex includes:

  • laser gas analyzer "LGAU-02";
  • remote control unit with sound signal sources;
  • additionally: a personal computer with installed software.


Figure: one

A diagram of the organization of an auto laboratory is presented for finding leaks from underground gas pipelines is presented in Fig. 1 In an air laboratory, you can do without a flow stimulator, providing an effective air intake by the pressure of the outside air, and on a hand trolley, you can use an external sampler instead of a surface sampler.

The advantages of the LGAU-02 gas analyzer are manifested when solving problems:

  • detection of leaks from underground gas pipelines of city gas networks, as well as from main and distribution pipelines using an auto laboratory that performs measurements on the go;
  • detecting leaks from underground, surface and air pipelines using a hand trolley that takes measurements on the go;
  • detection of leaks from main gas pipelines using an aviation laboratory;
  • measuring variations in the methane (hydrocarbon) background over large areas (hydrocarbon survey) using an airborne laboratory in order to search for oil and gas fields and environmental control of the atmosphere.


Figure: 2

  • The software allows you to maintain archives. An event log is also kept.

Functionality of the complex

  • The gas analyzer is made in the form of an optoelectronic measuring unit in a dust- and splash-proof IP54 case and is equipped with a remote control panel equipped with an analog indicator, a single zero setting button and a two-stage sound and light signaling of increased concentrations with adjustable response thresholds. Ease of installation and maintenance of the device, high reliability, small size and power consumption allow it to be used autonomously, on handcarts, cars and on board almost any aircraft carrier, including hang gliders and mini planes. The gas analyzer can operate completely autonomously, and instead of the remote control, any DC voltage measuring device from 0 to 5 V can be connected. Documentation of measurement data and plotting in real time can be carried out on a regular personal computer with RS 232C interface, including portable. When connected to the gas analyzer-computer satellite navigation system, it is possible to map the gas contamination field. The flow rate generator can be connected via a special button for switching the supply voltage on the front panel of the device.

Operating experience

  • Operating experience. Since 1998 the Lengaz St. Petersburg City Gas Industry and since 2004 the Moscow State Unitary Enterprise Mosgaz have been operating auto labs to search for natural gas leaks from urban underground gas pipelines based on LGAU-02. The prototypes of the device were used as part of air laboratories during the atmogeochemical survey in the complex of gas and oil exploration works in Tatarstan, Chuvashia and in the north of the Krasnoyarsk Territory and during the environmental examination of the atmosphere in the cities of Tula and Moscow. In addition, the devices were used as part of auto laboratories for geoecological surveys of the territories of distribution of technogenic soils in a number of areas of mass development in Moscow, as well as autonomously - during ground geochemical surveys in Korea. On the basis of the gas analyzer, an onboard computerized complex for aviation hydrocarbon gas survey was created. In the 2001 field season, the flight time of the complex on board the An 2 aircraft exceeded 600 hours without a single failure of the device, and the total area covered was about 30 thousand square meters. km.

Prospects for the development of the complex

  • Implementation of additional USB interfaces;
  • Connecting a GPS satellite navigation device with an interactive terrain map;
  • Implementation additional opportunities at the request of the user.
Publications

Journal "Instruments and Experiment Technique", 1999, No. 5

Laser gas analyzer for finding gas leaks from underground gas pipelines

Journal "Instruments and Control Systems", 1998, No. 9

Onboard laser absorption hydrocarbon gas analyzer

Copyright 1998-2005 Engineering Center MEPhI

Usage: control of harmful substances in the air. The essence of the invention: the device contains a laser gas discharge tube, a beam forming unit made in the form of a diffraction grating on a piezo corrector, which are located in a tangential unit associated with a stepping motor, an optoacoustic cell, a reference cuvette, a measuring and background microphone, and two pyroelectric sensors, connected through an analog-to-digital converter and an interface unit to the input of a personal computer. 1 ill.

The proposed invention relates to measuring technology and is intended for monitoring harmful substances in the air. Lists of harmful substances in the air of the working or living area have hundreds of substances that affect the human body. Many devices are known, for example, serving to control the composition of air using various measurement methods: chemical-analytical, chromatographic, coulometric, etc. One of the most suitable for performing operational measurements with the ability to control a large number of harmful substances is the method using the absorption of infrared radiation. Known gas analyzers of the GIAM type are designed to register one of the following gases: CO, CO 2, CH 4, SO 2, NO. Incandescent filaments (lamps) with a continuous spectrum of radiation are used as sources of infrared radiation. To isolate the spectral range corresponding to the absorption spectrum of the test substance, light filters are used. Measurements are carried out using a reference cell with a reference gas. The intermittent luminous flux is alternately directed to the working and comparative cuvettes, passing through which it (the luminous flux) is registered by an optoacoustic detector filled with the measured gas. The difference in signals from the detectors determines the concentration of the test substance in the air. Devices of this type, possessing good efficiency (the time for establishing readings is about 10 s), do not allow simultaneous (in one sample) registration of more than one component of pollutants. Known universal gas monitor 1302 firm Brüel & Kjr allows simultaneous registration of up to five impurities in one air sample. The device uses a filament as a source of infrared radiation. The change in the spectrum of infrared radiation falling into the sensitive volume of the optical-acoustic cell is presented automatically during measurements using a set of narrow-band light filters installed on a rotating disk. The air sample fills the volume of the optical-acoustic cell. For the duration of the measurement, the inlet and outlet of the cell is blocked from the outside air. Microphones are used to measure the amplitude of pressure fluctuations occurring in the cell when the intermittent light flux is absorbed by the sample under study. Measurements are made for each filter. The total measurement time for one sample is approximately 2 minutes. The measurement results determine the concentration of up to five impurities in one sample. The control of the device operation and processing of the measurement results is carried out using the built-in processor. The separately supplied set of two 2 replaceable narrow-band light filters allows the registration of a large number of impurities that absorb infrared radiation. However, the device allows measurements to be performed only with a priori known composition of pollutants. Otherwise, the overlap of absorption bands of various substances does not allow obtaining adequate information on the composition of harmful substances in the air. The closest to the proposed solution is a laser gas analyzer, described in and containing a laser gas-discharge tube, to which a high-voltage source and a cooling unit are connected, located on one optical axis, a beam forming unit and an optical-acoustic cell, to which an air intake unit, measuring a microphone and a pyroelectric sensor, an analog-to-digital converter connected via an interface unit and a data input and output unit with the input of a personal electronic computer. The output of which is connected through the interface unit to the input of the control unit. The use of a laser source of infrared radiation allows realizing a high spectral resolution in the device approximately (10-20 nm). The absorption in the test gas is recorded using an optoacoustic cell. The gas analyzer consists of three main parts: a source of tunable infrared radiation, an optical-acoustic cell (OAP), a system for recording and processing information. In the device, the beam forming unit is made in the form of an optically coupled modulator, shaper, mirror, focusing lens and diffraction grating. The selected in the device method of tuning the wavelength of laser radiation using a diffraction grating and a rotating mirror allows the selection of 36 radiation lines. The identification of emission lines is carried out only when setting up the device. When radiation is absorbed in the test gas filling the OAP, an acoustic wave is formed in it, which is recorded by a condenser microphone. Signals from a microphone and a pyroelectric radiation detector that records the power of laser radiation are fed to the input of a two-channel registration system consisting of two synchronous detectors. Analog recording of the registered signals is carried out using a recorder. Information can be read using a digital voltmeter and a computer. The disadvantages of the prototype are the limited number of radiation lines, which affects the multicomponent in one air sample, and the lack of control over the radiation wavelength. The objective of the invention is to provide a rapid multicomponent analysis of the composition of the air for harmful substances with high accuracy. This task is in a device containing a laser gas analyzer, containing a laser gas-discharge tube to which a high-voltage source and a cooling unit are connected, a beam forming unit, made in the form of a diffraction grating on a piezo corrector, and an optical-acoustic cell to which are connected an air intake unit and a measuring microphone, a pyroelectric sensor connected through a series-connected analog-to-digital converter and an interface unit to the PC input, is solved due to the fact that the gas analyzer additionally contains a background microphone, a reference cell located on one optical axis and an additional pyroelectric sensor connected similar to the main pyroelectric sensor, as well as a differential amplifier, in the beam-forming unit, the diffraction grating and the piezoelectric corrector are located in a tangential unit connected to the stepping motor, and the outputs of the measuring and background microphones connected through a differential amplifier to the ADC, the outputs of the control unit are connected to the corresponding inputs of the piezo corrector and the stepper motor of the beam forming unit, the output of the personal computer through the interface unit is connected to the control unit. The essence of the invention lies in the fact that the proposed implementation of the beam forming unit allows you to have a large (up to 70 lines of IR radiation) set of wavelengths with a fixed and controlled wavelength (multicomponent and accuracy); the software and the data bank used in the PC and its communication through the interface unit and the control unit with all the gas analyzer sensors ensure the promptness of the parameter drift correction and information processing. The drawing shows a block diagram of the gas analyzer. It contains a laser gas-discharge tube LGRT 1 (CO 2 -laser), a high-voltage power supply unit 2 LGRT, a cooling unit 3 serves to cool the LGRT, aperture 4 regulates the radiation power, a diffraction grating 5, the rotation of which changes the radiation wavelength, piezo corrector 6 compensates for temperature instability , tangential block 7, the longitudinal movement of which by 20 mm leads to a rotation of the diffraction grating 5 by 14 o, the stepper motor 8 moves the tangential unit 7, mirrors 9, directing IR radiation to the input window of the AOC, elements 4, 5, 6, 7 , 8 and 9 constitute a beam forming unit 26, a pyroelectric sensor 10, which receives IR radiation, partially reflected from the input window of the OAP, a pyroelectric sensor 11, which records IR radiation that passed through the OAP through a reference cell, a background microphone 12, not " seeing "the sensitive volume of the OAP, a measuring microphone 13, which records a periodic change in pressure in the OAP due to absorption of n intermittent luminous flux, optoacoustic cell ОАЯ 14, a sensitive element of the gas analyzer, reference cuvette 15 with a known filling, used to control the radiation wavelength, blower 16 supplying the test air to the ОАЯ, solenoid valves 17, 18 and 19, which regulate the flow of the test air, air intake (tube) 20, obturator 21, which serves to periodically interrupt the radiation flow, filter 22, temperature sensor 23 in the cooling system, pressure sensor 24 in the cooling system, pressure sensor 25 in the air intake circuit, PC 27 controls the operation and collection of measurement results, the interface unit 28 is connected by a highway with a PC 27, with a control unit 29, an analog-to-digital converter ADC 30, a PC 27 of the IBM PC type is provided with software 31 and a data bank 32 (shown conditionally). Signals 13 and 12 are subtracted from one another, the difference is normalized to the readings of the pyroelectric sensor 10. The measurements are carried out at wavelengths set from the PC 27 (each wavelength corresponds to a certain step of the stepper motor 8). The interface unit 28 serves to interface the PC 27 and the executive-registering part of the gas analyzer with the ADC 30, which converts the signals from the pyroelectric sensors 10, 11 and from the differential amplifier 33 into a digital code. The control unit 29 carries out the operation of the actuators of the blower 16, the piezo corrector 6, the stepper motor 8, the solenoid valves 17, 18 and 19. The control unit 29 also monitors the pressure and temperature in the cooling circuit of the LGRT 1 and controls the pressure in the air intake system. The sample is taken in the OAO 14 through the air intake pipe 20, filter 22. The air moves through the pipe 20 under the action of the blower 16. The flow direction is adjusted by valves 17, 18, 19. The pressure sensor 25 serves to check the serviceability of the air intake system. In the measurement mode, part of the radiation is absorbed by the gas under study in the OAD 14, causing periodic pressure fluctuations with a frequency equal to the frequency of interruption of the radiation beam by the shutter 21, which are recorded by the microphone 13. Part of the radiation, having passed through the exit window of the OAO 14, enters the reference cell 15, and then to the pyroelectric sensor 11. During processing, signals from the differential amplifier 33 (whose inputs are connected to microphones 12 and 13) and the pyroelectric sensor 11, normalized to the readings of the sensor 10, are used. using specially developed software 31 and databank 32. The operation of the gas analyzer, the operator and the functionality of the programs is described below. Work with the gas analyzer begins with connecting the PC 27 to the network and downloading the SCO 2 software containing following programs : 1. CONTROL; 2. TEST 3. TEST LINE; 4. SPECTRA; 5. CALCULATION; 6. RESULT; 7. BANK. After loading SCO 2, the message "ON THE GAS ANALYZER" appears on the display screen of the PC 27, the "CONTROL" program is turned on, providing a check of the functioning of the gas analyzer before starting measurements. The obturator 21, the supercharger 16, the valves 17, 18 and 19 are checked. Further, in accordance with the "CONTROL" program, the display shows the query "PERFORM TEST MEASUREMENT". If a test measurement is required, confirmed by pressing the D key, the operator performs the work according to the "TEST" program. The message "FILL OAU WITH ZERO GAS" appears on the display screen. "READY", after filling with the D key, the measurement program starts: measurements are taken of the signals of microphones 12 and 13, of the pyroelectric power sensor 10 at different values \u200b\u200bof the radiation lines (i.e. at different values \u200b\u200bof the step number of the stepper motor 8. The results are entered into the PC memory 27 for use in the program "CALCULATION"). After that the message "TAKE ZERO MEASUREMENT" appears on the screen. If no measurements are made with the "TEST" program, this message appears immediately. The measurements are carried out using the "TEST LINE" program by pressing the D key. Air is pumped through OAJ 14 by blower 16, valves 18 and 19 are closed, valve 17 is opened, after which blower 16 is turned off and signals are measured from microphones 12 and 13 connected to the differential amplifier 33, and pyroelectric sensors 10 and 11 with different numbers of steps of the stepper motor 8. The measurement results after ADC 30 are normalized to the readings of the pyroelectric power sensor 10. If measurements were not carried out using the "TEST" program, then the signals of microphones 12 and 13 are written to a file for processing in the "CALCULATION" program, otherwise they are not used further; the signal from the sensor 11 is entered into the file for the program of basic measurements "SPECTRA". At the end of the program, the prompt "SCAN OPERATION MODE" appears on the display screen. When you press the D key, the work will be carried out according to the "SPECTRA" program with the measurement of signals from microphones 12 and 13 and from a pyroelectric sensor 10 in the entire radiation range, at each group of steps corresponding to the presence of radiation. In this case, to control the radiation spectrum, the measurement results are compared with the measurements from the sensor 11 and the data on the gas absorption spectrum in the reference cell 15 entered into the data bank during the calibration of the gas analyzer. If necessary, an amendment is made to the numbering of steps specified by the "SPECTRA" program. The measurement results are entered into a file for the "CALCULATION" program. In case of refusal to work in the scanning mode (pressing the "H" key) the message "INPUT THE NAMES OF CONTAMINANTS FROM THE NAMED LIST" appears, the work continues according to the "SPECTRA" program. A list of contaminants appears on the screen. After selecting the pollutants, the message "OPERATING MODE SINGLE" appears. When the D key is pressed, a single measurement is carried out: an air sample OAYA 14 is collected, signals from microphones 12 and 13 and from the sensor 10 are measured on the absorption lines of the sought substances, determined by the step number of the stepper motor 8, taking into account the zero measurement. The measurement results are entered into a file for processing using the "CALCULATION" program. In case of refusal from a single measurement (pressing the H key) the message "SET THE MEASUREMENT TIME IN HOURS" appears, after which continuous measurements are carried out using the "SPECTRA" program for a specified time. The interval between individual measurements is 5 min. The measurement results are entered into a file for processing using the "CALCULATION" program. The processing of the measurement results is carried out according to the "CALCULATION" program at the end of the measurements (single mode), between separate measurements (continuous mode). Processing is carried out using a databank (BANK program), which contains instrumental gas absorption spectra, sensitivity to each individual gas, minimum detectable quantities, gas absorption spectrum of a reference cuvette, maximum permissible concentrations of DNA gases for air in the working and living areas. The results are displayed in the form of a table (single measurements) or a graph (continuous measurements) in comparison with the MPC. In case of uncertainty in the processing results (for example, coincident absorption spectra), a message is displayed about the inadequacy of measurements. Thus, the proposed gas analyzer provides technical means for rapid determination of the absorption peaks of various air impurities (up to 60 components in one sample), the impurity concentration is determined by the magnitude of the absorption peak, which favorably distinguishes it from analogues and the prototype.

CLAIM

A laser gas analyzer containing a laser gas discharge tube to which a high-voltage voltage source and a cooling unit are connected, a beam forming unit located on the same optical axis with the laser gas discharge tube, made in the form of a diffraction grating on a piezo corrector, and an optoacoustic cell (OAP), to which the unit is connected air intake and a measuring microphone, a pyroelectric sensor connected through a series-connected analog-to-digital converter (ADC) and an interface unit to the input of a personal computer, characterized in that the gas analyzer additionally contains a background microphone, located on the same optical axis with an optical-acoustic cell, a reference cuvette and an additional pyroelectric sensor connected similarly to the main pyroelectric sensor, as well as a differential amplifier, in the beam-forming unit, a diffraction grating and a piezoelectric corrector are located in a tangential unit associated with a stepping motor, A rotary mirror is installed in the genetic unit, which directs radiation to the input window of the OAD, and the outputs of the measuring and background microphones are connected to the ADC through a differential amplifier, the outputs of the control unit are connected to the corresponding inputs of the piezo corrector and the stepper motor of the beam forming unit, the output of the personal computer through the interface unit is connected to the unit management.

Chapter 1. The method of optical-acoustic spectroscopy

1.1. Laser optical-acoustic gas analyzer "LAG-1"

Chapter 2. Route differential absorption gas analyzers

2.1. Long Path Differential Absorption Method

2.2. Analysis of informative spectral ranges for sounding of IGM by MIS

2.3. Performance characteristics of parametric converters

2. 4. Choice of informative wavelengths

2. 5. Gas analyzer "Resonance-3"

2. 5. 1. Registration block

2. 6. Gas analyzer "Tral"

2. 7. IR laser gas analyzers "Tral-3" and "Tral-Zm"

2. 8. Laser gas analyzer "Tral-4"

2. 8. 1 "Tral-4". Results of field measurements

2. 9. "Resonance-3", "Trawl". Results of field measurements of the IGM of the atmosphere

Chapter 3. Remote laser monitoring of the ozonosphere with a differential absorption lidar

3.1 Methods for reducing the dynamic range of a lidar signal

3.2 Taking into account the “sticking” factor of one-electron pulses

3.3 Sounding channel of the vertical distribution of ozone SLS based on a mirror 0 0.5 m.

3.4 Software package "ATOS"

3.5 Climatology and trends of stratospheric ozone over Tomsk for the period 19962003

3.5.1. Intra-annual variability of stratospheric ozone

3.5.2. Interannual variability and trends in stratospheric ozone

3.6 Comparison of lidar and satellite data on VOD profiles 102 Conclusion 104 References

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Dissertation introduction (part of the abstract) on the topic "Laser gas analyzers based on the differential absorption method"

The urgency of the problem. The most important problem of our time is environmental protection. The environment undergoes changes under the influence of various factors. Together with various natural phenomena (volcanic eruptions, forest fires, soil erosion, etc.), human activities are becoming increasingly important in the process of influencing the environment. The rapid development of industry, energy, agriculture and transport has led to an increasing anthropogenic impact on the environment. A number of harmful by-products in the form of aerosols, gases, domestic and industrial waste waters, oil products, etc., enter the atmosphere, hydrosphere and lithosphere, which negatively affect the biological conditions of human existence and the biosphere as a whole.

In the industrially developed regions of many countries, the content of harmful substances in the atmosphere sometimes exceeds the maximum permissible standards. The main sources of pollution are: a) Powerful thermal power plants operating on solid, liquid or gaseous fuels. The generation of electricity in coal-fired thermal power plants entails the release of ash, sulfur dioxide and nitrogen oxides into the atmosphere. Power plants operating on natural gas do not emit ash and sulfur dioxide into the atmosphere, but nitrogen oxides are emitted in large quantities. b) Enterprises of ferrous and non-ferrous metallurgy. Steel smelting is associated with the emission of dust, sulfur dioxide and carbon monoxide into the atmosphere. c) Chemical industry enterprises that emit into the atmosphere a much smaller amount of harmful substances in comparison, for example, with metallurgical enterprises, however, a wide variety of chemical industries and their proximity to settlements often make these emissions the most dangerous. It is known, for example, that enterprises of the chemical industry emit into the atmosphere more than 100 especially harmful chemical compounds characterized by high toxicity, for which maximum permissible concentrations (MPC) have been established. d) A serious danger to the health and life of people is posed by harmful substances emitted by cars that enter the exhaust gases, which make up about 60% of all toxic impurities that pollute the air of industrial centers. The exhaust gases of vehicles include a wide range of toxic substances, the main of which are carbon monoxide, nitrogen oxides, hydrocarbons, carcinogenic substances, including 3,4-benzopyrene, sulfurous gases, products containing lead, chlorine, bromine and sometimes phosphorus. ...

Since it was discovered that the chlorine cycle can play a significant role in the balance of stratospheric ozone, the attention of researchers has been drawn to the possible accumulation of fluorochlorocarbons (freons), which requires control of their content, in the troposphere and especially in the stratosphere, where they are involved in the destruction of the ozone layer. planets - the only shield of all living things from the hard ultraviolet radiation of the Sun. Freons enter the atmosphere both directly from aerosol containers and in accidents from refrigeration units, air conditioners, etc.

A serious problem is the accumulation of so-called greenhouse gases in the atmosphere: water vapor, carbon dioxide, methane, etc. (monitoring of which is also necessary), which leads to an increase in ambient temperature and climate change. Thus, the content of methane in the atmosphere is growing quite rapidly - since the beginning of the industrial period, it has grown by about 150%, while the content of carbon dioxide has increased by only 30% (for both gases, the rate of increase in concentration was rather low until the second half of the 20th century and significantly increased in recent decades).

The consequences of this process can be catastrophic for our planet.

Almost all gas constituents of the Earth's atmosphere, except nitrogen, oxygen, and argon, are usually referred to as the so-called minor gas constituents (MGS). The percentage of IGM in the atmosphere is small, but the increase in their content due to the anthropogenic factor has a significant impact on many processes occurring in the atmosphere.

The microclimate changes under the influence of the polluted atmosphere; accelerated destruction of metal and reinforced concrete structures (millions of tons of metal and other materials are lost annually from corrosion, the corrosion rate of metals in rural areas is 4-5 times lower than in industrial areas); acidification of soils; poisoning and death of vegetation, animals and birds; chemical destruction of buildings and structures, monuments of architecture and art.

A large range, a large volume of pollutants emitted into the atmosphere, the complexity of physical and chemical processes occurring in nature, an insufficiently clear understanding of the degree of influence of a particular substance on the environment, do not allow an accurate assessment of the damage caused by humans to the environment. To develop scientifically based conclusions and predict changes in the state of the Earth's atmosphere in individual regions and on a global scale, regular measurements of the concentration of its gas constituents with existing instruments and the development of new methods and means of observation are needed.

State of the issue. A wide variety of methods are currently used to control the atmosphere:

In addition to a large group of chemical methods of gas analysis, gas analyzers used in practice use a change in the thermal conductivity of various gases and vapors depending on their concentration, or measure the amount of heat proportional to the amount of the analyzed component released (absorbed) as a result of a certain chemical reaction in thermal gas analyzers;

The group related to electrical includes: ionization, electrochemical and electroconductometric (measured specific electrical conductivity of electrolytes depending on the concentration of the investigated component);

Chromatographic gas analyzers use the different ability of individual gas components to be sorbed and desorbed by a solid or liquid sorbent;

In mass spectral gas analyzers, the time and spatial division into groups of ions of different mass (preliminary ionization of neutral atoms and molecules is carried out), contained in the sample, takes place, and the ion current formed by the total charge of particles of the same mass and characterizing their relative content is measured;

Optical gas analyzers use the dependence of the optical properties of the investigated gas mixture (optical density, spectral radiation and absorption, refractive index) on its concentration. Optical includes absorption, spectrophotometric, photocolorimetric, luminescent, nephelometric and others. ...

As a rule, all of these methods require sampling, which introduces additional errors in the measured value. Practically only some of the optical methods allow remote measurements, promptly obtain information about the integral and local content of the measured component, and carry out contamination mapping. The advent of the laser gave impetus to the further development of optical methods. The unique capabilities of lasers have allowed methods using laser radiation to take a special place among optical and other methods of gas analysis.

Laser methods are characterized by: high concentration sensitivity (as a rule, measurements are carried out at or below background concentrations), efficiency (the time required for measurement is several times less than for other methods), distance (the ability to receive information from objects from distances of hundreds, thousands and even tens of thousands of meters from the measuring system), high (up to tens of meters) spatial-temporal resolution. Laser gas analyzers used for monitoring use such interactions of optical radiation with the medium under investigation as: resonant absorption, elastic and Raman scattering, and fluorescence. Resonant absorption has the largest interaction cross section. This is what determines the high sensitivity of laser gas analyzers operating by the \\ / differential absorption method. For the first time in 1964, this method was proposed by Scotland for measuring high-altitude moisture profiles. Since then, lidar and trace measurements of ozone (Uchino et al. Japan, Kuemi University), SO2 (Grant et al. USA) and some other IGM have been implemented in practice. With the development of laser technology in our country and abroad, optical-acoustic (for local gas analysis) and route (giving integral values \u200b\u200bof the concentration of the gas under study) laser gas analyzers began to develop, as well as lidars (LIDAR - an abbreviation of the English words Light Detection and Ranging), giving information with space-time resolution to study the concentration of IGM in the atmosphere. But at the beginning of work on the dissertation, with rare exceptions, all of them were designed to measure one, maximum two gas components, or were laboratory models, while environmental monitoring requires a multicomponent gas analysis on fairly long routes (along city highways, territory large industrial enterprises).

As is clear from the literature, the mid-IR region of the spectrum is most suitable for the purposes of laser gas analysis of the IGM. The main vibrational-rotational bands of the majority of IGMs are located here. There are allowed structures and individual absorption lines of almost all atmospheric gases with the exception of simple ones, such as N2, O2, H2.

In the mid-IR range of the spectrum, as is known, highly efficient molecular lasers emit: CO, CO2, NH3, HF, DF and others. Of these, the most reliable and acceptable for the purpose of gas analysis are highly efficient CO lasers. In addition to the traditional 9.6 and 10.6 μm bands, these lasers can generate sequential bands shifted relative to the traditional ones by about 1 cm "1, as well as the main 4.3 μm band and hot emission lines. and CO2 isotopes to obtain an additional set of shifted lasing lines, then we obtain a rich set of emission lines for this laser source.

Recently developed highly efficient parametric frequency converters based on nonlinear crystals ZnGeP2, CdGeAs2, TlAsSe3, AgGaSe2, etc. have made it possible to obtain the second, third and fourth harmonics of COr laser radiation, as well as the total difference frequencies of two CO2 and other lasers, such as CO , NH3, Erbium, etc. For laser sounding of atmospheric IGMs, it is important that most of these emission lines, including transformed ones, fall within the spectral transparency windows of the atmosphere.

Thus, a low-pressure molecular CO2 laser equipped with a set of thresholdless parametric frequency converters made of ZnGeP2, CdGeAs2, TlAsSe3, and AgGaSe2 satisfies most of the following requirements. The distance between adjacent lines of such lasers is approximately 1.5-2 cm "1, which simplifies the problem of spectral selection and their frequency tuning. Applying a two-stage conversion, for example, of a CO2 laser or the sum-difference frequencies of two CO2, or CO2 and CO2 lasers and their harmonics, it is possible to very tightly, with a step up to 10 ^ cm "1, cover the range from 2 to 17 microns. The position of the centers of the emission lines of the pump lasers and the rather narrow spectral width (2x 10 "3 cm" 1) are provided by the physical parameters of the active medium. The position of the centers of the lines, and, consequently, the position of the emission lines of the converted frequencies are known with a very high accuracy, which removes the problem of controlling the spectral characteristics. The efficiency of such converters is quite high and ranges from tenths to tens of percent, which makes it possible to create route gas analyzers using topographic objects and atmospheric aerosols as reflectors.

Another informative spectral range for laser gas analysis is the UV region. There are strong electronic bands of many polluting gases here. Unlike the mid-IR region of the spectrum, the UV absorption bands are nonselective and mutually overlapped. The greatest development in this area was obtained by the ozonometric method due to the presence here of the Hartley-Huggins ozone absorption band.

The ability to perform spatially resolved measurements of atmospheric ozone with a lidar was first shown in 1977 (Meger et al). And, since the second half of the 1980s, laser sounding of the ozonosphere has become a regular feature at a number of observatories. It provides information on the vertical distribution of ozone (VOD), successfully complementing such information obtained by the contact method using ozonesondes and rockets, especially above 30 km, where ozonosondes data become unrepresentative.

The Siberian Lidar Station has been monitoring the ozonosphere since December 1988. During this period, the lidar technology was constantly improved, the measurement and data processing methods were developed and improved, software for controlling the measurement process, new software packages for processing the results obtained were created.

Objective. Development of gas analyzers based on the differential absorption method for detecting and measuring the concentration of MGM and determining their space-time distribution in the atmosphere.

In the course of the work, the following tasks were performed;

Development of an optical-acoustic gas analyzer for local gas analysis and study using it of the spatial distribution of hydrocarbons and other gas mixtures;

Development and creation of path laser gas analyzers for studying the gas composition of the atmosphere;

Development of methods for measuring IGM in the atmosphere;

Full-scale testing of the developed devices based on the developed measurement techniques;

Study of the temporal dynamics of IGM in ecologically clean regions of the country subject to significant anthropogenic load;

Creation of a channel for sensing the vertical distribution of ozone (VOD) in the stratosphere (based on the receiving mirror 0 0.5 m) CJIC;

Monitoring the state of the ozonosphere in routine measurements; - study of the climatology of the ozonosphere, assessment of trends in stratospheric ozone.

The following are submitted for defense:

1. The developed laser optical-acoustic gas analyzer "LAG-1", which allows, on the basis of the developed technique, to separately measure the concentration of methane and heavier hydrocarbons in air mixtures of natural and associated oil gases with any ratio of components in the mixture.

2. Developed layouts of laser gas analyzers of the TRAL series, in the mid-IR range of the spectrum, allowing to quickly measure the concentration of more than 12 gases at and below the MPC on paths up to 2 km long using a mirror or topographic retroreflector.

3. The UV ozone lidar created by the author based on the excimer XeC1 laser, which provided uninterrupted long-term sounding of the ozonosphere over Tomsk at the Siberian lidar station in the altitude range of 13-45 km with a maximum vertical resolution of 100 m.

Scientific novelty of the work.

For the first time, the informative wavelengths of the atmospheric IGM sounding were selected and experimentally tested;

A number of unique mobile and stationary path-line gas analyzers based on tunable molecular lasers with radiation frequency converters have been created, which make it possible to quickly carry out multicomponent analysis of the gas composition of the atmosphere;

Measurements of daily variations in the concentration of MGM (such as C2H4, NH3, H2O, CO2, CO, O3, N0, etc.) in ecologically clean regions of the country subject to significant anthropogenic load have been carried out;

For the first time, the climatological features of the ozonosphere over Tomsk were determined on the basis of regular and long-term measurements of the profiles of the vertical distribution of ozone;

Using the results of work. The data obtained using gas analyzers were presented to the USSR Olympic Committee in 1979-1980. in Moscow, as well as to environmental organizations in the city of Tomsk, Kemerovo, Sofia (NRB). They were included in the final reports of the IAO SB RAS on various RFBR grants, agreements, contracts and programs, for example, TOR (tropospheric ozone research), SATOR (stratospheric and tropospheric ozone research) and others.

The practical value of the work is as follows:

An optical-acoustic gas analyzer has been developed, which allows to measure with high accuracy the concentration of both the sum of hydrocarbons of the methane group and separately methane and heavier hydrocarbons in a mixture of natural and associated petroleum gases. With the help of this gas analyzer, it is possible to search for oil and gas by gas halos of gases coming out to the surface of the earth over hydrocarbon fields;

The developed route gas analyzers make it possible to measure the concentration of gas mixtures at and below the MPC from a wide list of priority polluting gases;

A channel for probing the vertical distribution of ozone CJIC has been created on the basis of a 0 0.5 m receiving mirror, which makes it possible to obtain reliable VOD profiles in the altitude range of 13-45 km with a maximum resolution of 100 m.

The reliability of the results of the work is ensured by: -good agreement of the experimental data obtained using the developed gas analyzers and the data obtained simultaneously by other methods, as well as; data; obtained by other authors in similar climatic and ecological conditions;

Good coincidence of the VOD profiles in the stratosphere measured by the lidar, ozonosondes data, as well as satellite measurements within the error of the devices used | (15 %).

Personal contribution. The work uses the results obtained either by the author personally or with his direct participation. This is the author's participation in the development of both general schemes for the construction of gas analyzers, and their individual optical-mechanical and electronic assemblies and blocks, in carrying out installation and commissioning works. The development of measurement techniques, test and expeditionary ^ and field tests of the created gas analyzers, also presented in the work, took place with the direct participation of the author. Since 1996, practically all observations of the state of the ozonosphere at the CJIC were carried out with the active participation of the author. He created an improved CJIC channel for sensing the vertical distribution of ozone on the basis of a XeC1 laser and a 0 0.5 m receiving mirror. The reanalysis of the RFO data carried out by the author made it possible to determine the specific features of the climatology of the ozonosphere over Tomsk.

The development process of gas analyzers, their test tests, processing of the results obtained during expeditionary work, the long-term accumulation of such a large amount of empirical information on BPO and its analysis could not have been carried out without the active participation of the whole team, without which this dissertation work would not have taken place. The statement of the problem and scientific guidance at different stages were carried out by Corresponding Member. RAS Zuev V.V. and Ph.D. Khmelnitsky G.S. The development of gas analyzers and their test and field tests were carried out jointly with the doctor of physical and mathematical sciences. Andreev Yu.M., Doctor of Physics and Mathematics Geiko P.P., researcher Shubin S.F. Theoretical work on the search for informative wavelengths was carried out by Ph.D. Mitselem A.A., D.Sc. Kataev M.Yu., Ph.D. Ptashnikov I.V., Ph.D. Romanovsky O.A. Lidar VOD measurements were carried out jointly with senior researcher A.V. Nevzorov, Ph.D. Burlakov V.D. and d.ph.-m.s. Marichev V.N., and processing of sounding data together with Ph.D. Bondarenko SL. and d.ph.-m.s. Elnikov A.V.

Approbation of work. The main results on the topic of the dissertation, obtained by the author, were published in 11 articles in Russian scientific peer-reviewed journals, reported at: VI, VII and XI All-Union symposia on laser and acoustic sounding (Tomsk, 1980, 1982, 1992); VI All-Union Symposium on the Propagation of Laser Radiation in the Atmosphere (Tomsk, 1881); XII All-Union Conference on Coherent and Nonlinear Optics (Moscow, 1985); V International Schools: I Seminar on Quantum Electronics. Lasers and their application (NRB, Sunny Beach, 1988); 5th Scientific Assembly of the International Association for Atmospheric Physics and Meteorology (Reading, UK, 1989); XI Symposium on Laser and Acoustic Sounding (Tomsk, 1992); And, III, IV and VI Inter-republican symposia "Optics of the atmosphere and ocean" (Tomsk, 1995, 1996, 1997 and 1999); III Siberian meeting on climate and environmental monitoring (Tomsk, 1999); I Interregional meeting "Ecology of Siberian rivers and the Arctic" (Tomsk 1999); VII International Symposium on Atmospheric and Oceanic Optics (Tomsk 2000); VIII and IX International Symposia on Atmospheric and Ocean Optics and Atmospheric Physics (Tomsk 2001 and 2002); 11 Workshop on Atmospheric Radiation Measurements (Atlanta, USA 2001); IX Working Group "Aerosols of Siberia" (Tomsk 2002); 21 and 22 International Laser Conference (Quebec, Canada, 2002, Matera, Italy 2004); II International conference "Environment and ecology of Siberia, the Far East and the Arctic" (Tomsk 2003); International Conference on Optical Technologies for Atmospheric, Oceanic and Environmental Research (Beijing, China 2004).

The structure and scope of the thesis. The dissertation work consists of an introduction, three chapters and a conclusion. The volume of the thesis is 116 pages, it contains 36 figures, 12 tables. The list of used literature contains 118 titles.

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Thesis conclusion on the topic "Devices and methods of experimental physics", Dolgiy, Sergei Ivanovich

Conclusion

In the course of the dissertation work, the author as part of the team did the following:

An optical-acoustic gas analyzer for local gas analysis has been developed, with its help a study of the spatial distribution of -hydrocarbons (during several expeditions on a motor ship) in areas where oil fields are located. The measured increase in the content of hydrocarbons in air samples in the area of \u200b\u200boil fields confirmed the hypothesis of the presence of gas halos over hydrocarbon fields and the prospects of using this gas analyzer for searching for oil and gas fields;

A complex of path laser gas analyzers operating in the IR region of the spectrum by the method of differential absorption and making it possible to measure the concentration of more than 12 gases at and below the MPC has been developed and created;

The technique of measuring the IGM in the atmosphere has been worked out;

Full-scale tests of the developed devices were carried out;

The pairs of informative wavelengths were experimentally checked and conclusions were drawn about their suitability for the purposes of gas analysis according to MIS;

Studies of the temporal dynamics of the IGM in ecologically clean regions of the country subject to significant anthropogenic load have been carried out;

Comparative measurements of MGM concentrations were carried out by the developed laser gas analyzers and devices operating on the basis of standard methods, which showed good agreement of the results obtained;

A channel for probing the vertical distribution of ozone (VOD) in the stratosphere (based on the 0 0.5 m receiving mirror) CJIC has been created, which has provided reliable VOD profiles over Tomsk over a long period of time, confirmed well in agreement with satellite and ozone probe data. This made it possible to carry out climatological studies and evaluate trends in stratospheric ozone, which showed that in the lower stratosphere at altitudes below 26 km, intra-annual changes in ozone concentrations are characterized by a maximum in spring and a minimum in autumn, and at altitudes above 26 km, the maximum shifts to the summer, and the minimum to winter. ... At an altitude of 26 km, in the area of \u200b\u200bwhich the cycle pause is located, the ozonosphere is divided into two parts: at the bottom, its behavior is determined mainly by dynamic processes, and at the top, by photochemical processes. A more detailed consideration of the intra-annual variations in VOD makes it possible to single out the following points: a) at an altitude of 14 km, where, apparently, the influence of fluctuations in the tropopause height is still significant, a localized maximum is not observed; b) in the range up to 18 km inclusive, the maximum seasonal fluctuations occur in February, and in the range of 20-26 km - in March; The greatest correspondence of the intra-annual variations in the VOD with the annual TOC variation is observed in the altitude range of 20-24 km, especially at an altitude of 22 km. c) at all heights, the BPO trends were statistically insignificant. Moreover, in the lower part of the ozonosphere, they are characterized by weakly negative values, and in the upper part, by weakly positive ones. In the area of \u200b\u200blocalization of the stratospheric ozone maximum 20 km), the values \u200b\u200bof negative trends are small (-0.32% per year). These results are consistent with an insignificant statistically insignificant TO trend (0.01 + 0.026% per year) over the same six-year period.

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