CN108107017A - Method based on the distribution of terahertz detection high-risk chemical - Google Patents
Method based on the distribution of terahertz detection high-risk chemical Download PDFInfo
- Publication number
- CN108107017A CN108107017A CN201711329777.2A CN201711329777A CN108107017A CN 108107017 A CN108107017 A CN 108107017A CN 201711329777 A CN201711329777 A CN 201711329777A CN 108107017 A CN108107017 A CN 108107017A
- Authority
- CN
- China
- Prior art keywords
- risk chemical
- concentration
- air high
- target acquisition
- information
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 239000000126 substance Substances 0.000 title claims abstract description 205
- 238000001514 detection method Methods 0.000 title claims abstract description 118
- 238000000034 method Methods 0.000 title claims abstract description 47
- 238000012545 processing Methods 0.000 claims description 14
- 238000004590 computer program Methods 0.000 claims description 2
- 239000000203 mixture Substances 0.000 abstract description 2
- 239000007787 solid Substances 0.000 abstract description 2
- 239000002341 toxic gas Substances 0.000 description 26
- 239000007789 gas Substances 0.000 description 19
- 238000005259 measurement Methods 0.000 description 9
- 239000000523 sample Substances 0.000 description 9
- 238000005070 sampling Methods 0.000 description 8
- 238000005516 engineering process Methods 0.000 description 6
- 238000005086 pumping Methods 0.000 description 6
- 230000008859 change Effects 0.000 description 5
- 238000010586 diagram Methods 0.000 description 4
- 238000010521 absorption reaction Methods 0.000 description 3
- 239000013626 chemical specie Substances 0.000 description 3
- 230000005684 electric field Effects 0.000 description 3
- 239000004744 fabric Substances 0.000 description 3
- 239000004615 ingredient Substances 0.000 description 3
- 241000894007 species Species 0.000 description 3
- 230000003595 spectral effect Effects 0.000 description 3
- 239000002131 composite material Substances 0.000 description 2
- 239000000428 dust Substances 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 238000004880 explosion Methods 0.000 description 2
- 239000008187 granular material Substances 0.000 description 2
- 238000003384 imaging method Methods 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 238000012544 monitoring process Methods 0.000 description 2
- 239000004071 soot Substances 0.000 description 2
- 238000001228 spectrum Methods 0.000 description 2
- 238000001328 terahertz time-domain spectroscopy Methods 0.000 description 2
- 238000012360 testing method Methods 0.000 description 2
- 238000000411 transmission spectrum Methods 0.000 description 2
- 241001269238 Data Species 0.000 description 1
- 238000005033 Fourier transform infrared spectroscopy Methods 0.000 description 1
- 241001463139 Vitta Species 0.000 description 1
- 230000002776 aggregation Effects 0.000 description 1
- 238000004220 aggregation Methods 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 230000008901 benefit Effects 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 230000001427 coherent effect Effects 0.000 description 1
- 238000004891 communication Methods 0.000 description 1
- 238000007405 data analysis Methods 0.000 description 1
- 230000003111 delayed effect Effects 0.000 description 1
- 239000003989 dielectric material Substances 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000002360 explosive Substances 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 230000005764 inhibitory process Effects 0.000 description 1
- 238000003780 insertion Methods 0.000 description 1
- 230000037431 insertion Effects 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 239000011159 matrix material Substances 0.000 description 1
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- 238000002044 microwave spectrum Methods 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 230000007096 poisonous effect Effects 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 230000001681 protective effect Effects 0.000 description 1
- 238000003908 quality control method Methods 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 230000002123 temporal effect Effects 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Classifications
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N21/00—Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
- G01N21/17—Systems in which incident light is modified in accordance with the properties of the material investigated
- G01N21/25—Colour; Spectral properties, i.e. comparison of effect of material on the light at two or more different wavelengths or wavelength bands
- G01N21/31—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry
- G01N21/35—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light
- G01N21/3581—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light using far infrared light; using Terahertz radiation
- G01N21/3586—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light using far infrared light; using Terahertz radiation by Terahertz time domain spectroscopy [THz-TDS]
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N21/00—Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
- G01N21/17—Systems in which incident light is modified in accordance with the properties of the material investigated
- G01N21/25—Colour; Spectral properties, i.e. comparison of effect of material on the light at two or more different wavelengths or wavelength bands
- G01N21/31—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry
- G01N21/35—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light
- G01N21/3504—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light for analysing gases, e.g. multi-gas analysis
Landscapes
- Physics & Mathematics (AREA)
- Spectroscopy & Molecular Physics (AREA)
- Health & Medical Sciences (AREA)
- General Physics & Mathematics (AREA)
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Analytical Chemistry (AREA)
- Biochemistry (AREA)
- General Health & Medical Sciences (AREA)
- Immunology (AREA)
- Pathology (AREA)
- Toxicology (AREA)
- Investigating Or Analysing Materials By Optical Means (AREA)
Abstract
The present invention relates to a kind of methods of terahertz detection air high-risk chemical distribution：The concentration distribution information of the air high-risk chemical of current detecting location is obtained by detection device；Target acquisition position is drawn according to the concentration distribution information, driving detection device marches to the target acquisition position；The air high-risk chemical concentration distribution information of the target acquisition position is obtained again, obtains the air high-risk chemical concentration distribution information of multigroup detecting location；By the invention it is possible to which realizing is needing to make the complex environment judged rapidly, can more elements such as air high-risk chemical composition, concentration, trend be subjected to solid and showed；It realizes the originally discrete concentration data progress continuous treatment for measuring and obtaining, crowd evacuation measure and malicious source suppressing method can quickly and effectively be made in air high-risk chemical leak scene by realizing.
Description
Technical field
The present invention relates to Environmental security field, more particularly to a kind of based on the distribution of terahertz detection high-risk chemical
Method.
Background technology
Usually, at explosion or attack of terrorism scene, it is high-risk often to there is the indefinite air of one or several kinds of ingredients
Chemicals.But due to the complexity of site environment, people are often difficult to determine that the ingredient of air high-risk chemical, air are high
The source of danger chemicals and the propagation path of air high-risk chemical, therefore can not quickly and effectively make crowd and dredge
The measure of dissipating and malicious source suppressing method, great loss is caused to the security of the lives and property of the people, and is the high-risk chemistry of air
The tracking and inhibition in product source eliminate work and bring many difficulties.
Existing gas detecting system is only limitted to demarcate air high-risk chemical species and its concentration, measure, and
Composite measurement cannot be carried out to the distribution situation of the air high-risk chemical leakage information in leakage region and intuitively showed, it is difficult
Commanding to be helped to formulate the Restrain measurement of gas leakage source and crowd evacuation scheme rapidly.
The content of the invention
Based on this, it is necessary in traditional technology, it is impossible to the air high-risk chemical leakage information in leak area
Distribution situation composite measurement and intuitively show, it is difficult to it is rapid formulate air high-risk chemical source of leaks Restrain measurement with
The problem of formulating crowd evacuation scheme, provide it is a kind of flexibly, intuitively probe gas spatial distribution method.
A kind of method based on terahertz detection high-risk chemical, the described method includes：
The concentration distribution information of the air high-risk chemical of current detecting location is obtained by detection device；
According to the air high-risk chemical concentration distribution acquisition of information target acquisition position, driving detection device is advanced
To the target acquisition position；
The air high-risk chemical concentration distribution information of the target acquisition position is obtained again；
Next target acquisition position is obtained according to the air high-risk chemical concentration distribution information of the target acquisition position
It puts, until the coordinate of next target acquisition position is overlapped with the coordinate of any detecting location before, obtains multigroup detection position
The air high-risk chemical concentration distribution information put；
The Gas concentration distribution information of multigroup detecting location is sent to data handling system to handle, is obtained
Air high-risk chemical spatial distribution image information.
In one of the embodiments, the detection device is terahertz time-domain system.
In one of the embodiments, the terahertz time-domain system is transmission-type terahertz time-domain system.
In one of the embodiments, the acquisition methods of next target acquisition position include：
All concentration distribution information acquired in three-dimensional coordinate are ranked up, obtain concentration highest in three-dimensional coordinate
The direction of point is the direct of travel of the driving device；
The driving device marches to next target acquisition position along the direct of travel.
In one of the embodiments, it is described to all concentration distribution information acquired in the three dimensions of current location
Be ranked up, including by Bubble Sort Algorithm to all concentration distribution information acquired in the three dimensions of current location into
Row sequence.
In one of the embodiments, it is described to be visited according to the air high-risk chemical concentration distribution information acquisition target
Location is put, and detection device is driven to march to the target acquisition position and is further included：
To the concentration information averaged in the different height of current location, the highest height of mean concentration is obtained as mesh
Absolute altitude degree；
The concentration of different angle in the highest height of the mean concentration is ranked up, obtains the mean concentration
The highest angle of concentration is the target angle of the driving device in highest height；
The detection device is driven to march to the target acquisition position according to the object height and target angle.
In one of the embodiments, the concentration information by multigroup a certain air high-risk chemical distribution transmits
The step of being handled to data handling system, obtaining air high-risk chemical spatial distribution image information includes：
Multigroup a certain air high-risk chemical is sent to numerical value compared with the concentration information that three-dimensional coordinate is distributed
Fitting system carries out numerical fitting, obtains a certain air high-risk chemical and believes compared with the continuously distributed concentration of three-dimensional coordinate
Breath；
The concentration information continuously distributed compared with three-dimensional coordinate is identified, obtains a certain air high-riskization
Product spatial distribution map；
In one of the embodiments, the air high-risk chemical concentration distribution information according to the current location,
The air high-risk chemical concentration distribution information of the target acquisition position, obtains air high-risk chemical spatial distribution image
It further includes afterwards：
Different types of air high-risk chemical is detected respectively by multiple detection devices, is obtained a variety of
The gas compartment distributed image of variety classes gas；
Different types of air high-risk chemical distributed image is overlapped processing, obtains variety classes air
High-risk chemical spatial distribution superimposed image, and the variety classes air high-risk chemical spatial distribution superimposed image is defeated
Go out.
In one of the embodiments, the concentration information continuously distributed compared with three-dimensional coordinate is subjected to color mark
Know.
A kind of computer readable storage medium, is stored thereon with computer program, which can when being executed by processor
The step of realizing any of the above embodiment.
Description of the drawings
Fig. 1 is the reflexive feedback system of Terahertz for the air high-risk chemical detection that one embodiment provides；
Fig. 2 is the structure chart of the telescope support that one embodiment provides and cantilever；
Fig. 3 is the transmission-type terahertz time-domain system that one embodiment provides；
Fig. 4 is the method flow diagram for the terahertz detection air high-risk chemical concentration distribution that one embodiment provides；
Fig. 5 is the method flow diagram for the single high-risk chemical source of leakage of terahertz detection that one embodiment provides；
Fig. 6 is the method flow diagram that the judgement detection device that one embodiment provides reaches source of leaks；
Fig. 7 is multiple high-risk chemical source of leaks detection method flow charts that one embodiment provides；
Fig. 8 is provided for one embodiment when detection tri- kinds of air high-risk chemicals of a, b, c, sets specific rotating shaft
The method flow diagram of the wicking height of rotation angle and telescope support；
Fig. 9 is a certain air high-risk chemical concentration result of detection distribution map that one embodiment provides；
Figure 10 is that a variety of air high-risk chemical concentration result of detection that one embodiment provides are distributed stacking chart.
Specific embodiment
In order to make the purpose , technical scheme and advantage of the present invention be clearer, it is right with reference to the accompanying drawings and embodiments
The present invention is further elaborated.It should be appreciated that specific embodiment described herein is only to explain the present invention, and
It is not used in the restriction present invention.
Referring to Fig. 1, a kind of reflexive feedback system of Terahertz of air high-risk chemical detection is provided in one embodiment
1000, described device includes：
Detection device 100, the detection device 100 are used for atmospheric sounding high-risk chemical information.
Specifically, detection device 100 is for being sampled to air high-risk chemical, and obtain the high-risk chemistry of air
The device of product Terahertz feature, air high-risk chemical information specifically includes air high-risk chemical concentration information and air is high
Danger chemical race category information.
Mechanic adjustment unit 110, the mechanic adjustment unit 110 is connected with the detection device 100, for adjusting
The height and orientation of detection device 100 are stated, to obtain the air high-risk chemical information of different height and orientation.
Mechanic adjustment unit 110 carries out the position of detection device 100 pair by mechanical structure according to the instruction of processor
It should adjust, height and orientation including adjusting detection device 100, be sat so as to change the three-dimensional of 100 stop places of detection device
It marks (x, y, z), including abscissa x, ordinate y and vertical coordinate z.Specifically, mechanic adjustment unit adjusts detection device 100
Three-dimensional coordinate, to obtain in three dimensions the air high-risk chemical concentration distribution under different three-dimensional coordinates, obtain (n, a,
B, c), including air high-risk chemical concentration n, abscissa a, ordinate b and vertical coordinate c.When detection device 100
In (x1,y1,z1) detect air high-risk chemical concentration distribution coordinate (n1,a1,b1,c1) when, then there is x1=a1,y1=b1,z1
=c1。
Moving bearing device 120, the moving bearing device 120 carries the mechanic adjustment unit 110, and drives institute
It states detection device 100 to move in space, to obtain the air high-risk chemical information of different position.
Wherein moving bearing device 120 can be mechanically connected with mechanic adjustment unit 110, and mechanic adjustment unit 110 can be set
In on moving bearing device 120, moved with the movement of moving bearing device 120.It is similar, mechanic adjustment unit 110 with
Detection device 100 is mechanically connected, and is moved with the movement of moving bearing device 120.Moving bearing device 120 passes through shifting
Dynamic mechanic adjustment unit 110 is carried out movement detector 100 and is moved in space, and moving bearing device 120 is for detection device
100 movement can be to move horizontally；Meanwhile mechanic adjustment unit 110 can adjust the height and orientation of detection device 100 simultaneously.
Processor 130, the processor 130 are used to handle the high-risk chemistry of air that the detection device 100 is detected
Product information, and according to the handling result of air high-risk chemical information feedback, that the mechanic adjustment unit is controlled to adjust is high
Degree, orientation and moving bearing device movement, and the air high-risk chemical information is handled.
Processor 130 be information receive center, Information Analysis Center, feedback information generation center, information dispatching centre with
And control centre, be realize air high-risk chemical detection system detection accuracy device.
In one of the embodiments, the moving bearing device includes babinet 121；The mechanic adjustment unit installation
On the moving bearing device, the processor 130 is located in the babinet 121.Specifically, mechanic adjustment unit can lead to
It crosses shaft 113 to be connected with moving bearing device, shaft can carry out 360 ° of rotations, so as to which mechanic adjustment unit be driven to carry out
360 ° of rotations.For example, shaft can carry out 360 ° of rotations in the horizontal direction, so that detection device 100 can be located
In different orientation, i.e., different (x, y) coordinates.In one of the embodiments, processor is placed in babinet 121, to processing
Device has protective effect.Specifically, the move mode of mobile bearing mode is unlimited, and moving bearing device 120 may include universal wheel
126, pulley and other can realize moving bearing device movement device or method all may be used.
In one of the embodiments, the processor 130 may include data processing module and control module, the number
Sort operation, the source of leakage that the computing carried out according to processing module includes carrying out the air high-risk chemical information are sentenced
Disconnected computing, data fitting operation, image superposition computing, coordinate coincidence judge computing, and the control module is used for according to the number
Instruction is sent to the air high-risk chemical spatial distribution detection device 100 according to the operation result of processing module, and drives institute
Air high-risk chemical spatial distribution detection device 100 is stated to be moved.
In one embodiment, the reflexive feedback system detection device 100 of Terahertz of air high-risk chemical detection is terahertz
Hereby time domain system, including air high-risk chemical sampling room 1021.
In addition, Terahertz air high-risk chemical detection system 1000 further includes feedback and instruction transmission electric wire 122, use
In the result of detection of reception detection device 100, and result of detection is transmitted to processor 130, and processor 130 is exported
Control instruction passes to moving bearing device and mechanic adjustment unit, and to control, moving bearing device is mobile, adjusts mechanical adjustment
Device, such as height of telescoping shoring column 113 etc..
Meanwhile Terahertz air high-risk chemical detection system 1000 may also include power set 124, the power dress
124 are put to may be disposed in moving bearing device 120；The power set 124 can be accumulator, be Terahertz air high-riskization
Product detection system provides power.
The detection device 100 may include terahertz time-domain system, and further, detection device 100 may include transmission-type too
Hertz time domain system, detects object for passing through THz wave.
Also referring to Fig. 2, in one of the embodiments, the mechanic adjustment unit 110 includes telescope support 114
With cantilever 112, telescope support 114 has card slot 1141, and card slot 1141 is used to cantilever 112 being fixed on telescope support 114；
Spring 1142 is provided in card slot 1141, spring 1142 controls the vertical height of cantilever to change by self-deformation, and then controls
Detection device height change.The telescope support is connected with the moving bearing device；It is stretched with described described 112 one end of cantilever
Contracting stent connects, and the other end is connected with the detection device 100.
Optionally, the connection mode of telescope support and cantilever is not limited to spring card slot connection, other can realize flexible branch
Frame control cantilever carries out the connection mode of height change.
Also referring to Fig. 3, a kind of terahertz time-domain system of air high-risk chemical, the time domain system are provided
Including：Laser generator 301, for generating pumping pulse and direct impulse；Delayer 307, for receiving laser generator
The 301 pumping pulse laser generated, and adjust the pumping pulse of the generation of laser generator 301 and the time delay of direct impulse.
Signal generator 302, for emitting terahertz signal；Terahertz detection device 303, for air high-riskization in environment
Product sampling detection；Signal receiver 304, for finishing receiving air high-risk chemical in high-risk chemical sampling room 1021
The terahertz signal of information detection；Signal processor 305 for being analyzed and processed to the terahertz signal received, obtains
Air high-risk chemical information.
In one embodiment, the laser generator 301 includes femtosecond laser 3011 and beam splitter 3012；The letter
Number generator 302 includes lens, for generating terahertz signal；The terahertz detection device 303 is high-risk to carry air
Sample chemicals 3031, the first off axis paraboloidal mirror 3032, the second off axis paraboloidal mirror 3033, the 3rd off axis paraboloidal mirror
3034th, the 4th off axis paraboloidal mirror 3035.Wherein, 3032 and second off axis paraboloidal mirror of the first off axis paraboloidal mirror
3033 are oppositely arranged, and the 3rd off axis paraboloidal mirror 3034 is oppositely arranged with the 4th off axis paraboloidal mirror 3035.The signal
Receiver 304 includes lens, for receiving terahertz signal；The signal processor 305 includes lock-in amplifier 3051 and letter
Number processing unit 3052；
In one of the embodiments, the femtosecond laser 3011 that femto-second laser is sent is divided into two beams by beam splitter 3012
Pulse is respectively pumping pulse and direct impulse.Wherein pumping pulse reaches delayer 307, after delayer 307, enters
It is mapped in lock-in amplifier 3051；The terahertz pulse that wherein direct impulse and signal generator 302 generate successively through the 3rd from
Axis paraboloidal mirror 3034, the first off axis paraboloidal mirror 3032 are incided on air high-risk chemical sample 3031, high-risk to air
Sample chemicals 3031 are detected, and are obtained result of detection signal, then are thrown off axis through the second off axis paraboloidal mirror the 3033, the 4th
3035 arriving signal receiver 304 of object plane mirror.Delayer 307 adjusts the time delay between pumping pulse and direct impulse, from
And change the time that detection light reaches terahertz detector.Utilize different detection light arrival times, Terahertz electric field strength
The amount of changing with time can be measured.Signal processing apparatus 3052 carries out the Terahertz electric field strength amount of changing with time
Analysis and processing, such as Fourier transformation is carried out, transmission spectrum is obtained, gained transmission spectrum is analyzed to obtain air height
The species and concentration information of danger chemicals；
In one of the embodiments, air high-risk chemical sample 3031 is placed in air high-risk chemical sampling room
In 1021 (not marked in figure), the air high-risk chemical sampling room 1021 in the terahertz time-domain system is in communication with the outside,
The terahertz time-domain system is used for the air high-risk chemical sample 3031 to the air high-risk chemical sampling room 1021
It is detected, obtains the air high-risk chemical information.In traditional technology, by air high-risk chemical be placed in gas chamber into
Row test, but during being detected by gas chamber, certain loss of THz wave, while the material of gas chamber can be caused
Certain property delayed of spectrum can be also caused, so that result of detection is inaccurate.
In toxic gas leakage scene or explosion scene, gas chamber sampling is often not easy to, and needs to obtain in real time, really
Live air high-risk chemical species and concentration levels, then detector is then needed to be placed directly in atmospheric environment and is carried out
The measurement of contact.
In one of the embodiments, air humidity tester is also installed on the terahertz time-domain system probe.Due to
Vapor is very strong for the absorption of Terahertz, therefore can select to eliminate vapor to result of detection using " making poor method "
Influence, gained Terahertz collection of illustrative plates will be detected and subtract the Terahertz collection of illustrative plates of the vapor of existing similary concentration in database, from
And the Terahertz profile information of corresponding air high-risk chemical to be measured is obtained, and then judge high-risk air high-risk chemical
Species and concentration information.
In one of the embodiments, testing time 20ps is chosen, the Terahertz of 1-2THz wave bands surveys air
Examination, obtains collection of illustrative plates；By Terahertz pop one's head on subsidiary air humidity tester atmospheric humidity is tested, obtain air
Relative humidity is 5%；For relative air humidity when being respectively 20ps in 5%, sampling time, water is in 1~3THz in called data storehouse
The absworption peak collection of illustrative plates of wave band；The collection of illustrative plates of measurement is subtracted into database collection of illustrative plates, you can obtain characteristic peak collection of illustrative plates；To characteristic peak collection of illustrative plates
In frequency and the peak height of fingerprint peaks carry out database and compare and calculate, you can obtain the high-risk substance of air under real time environment
Species and concentration.
Also referring to Fig. 4, a kind of high-risk chemical source of leaks detection method based on Terahertz, the described method includes：
S402 obtains the air high-risk chemical concentration distribution information of current location by detection device；
S404 according to the air high-risk chemical concentration distribution information acquisition target acquisition position, and drives detection to fill
It puts and marches to the target acquisition position；
S406 obtains the air high-risk chemical concentration distribution information of the target acquisition position again；According to the mesh
The air high-risk chemical concentration distribution information of mark detecting location obtains next target acquisition position；Obtain multigroup detection position
The air high-risk chemical concentration distribution information put；
The air high-risk chemical concentration distribution information of multigroup detecting location is sent at processing system by S408
Reason；Export air high-risk chemical spatial distribution image information.
In one of the embodiments, the detection device is terahertz time-domain system and device.
Specifically, THz wave is electromagnetic wave of the frequency in the range of 0.l~10THz (wavelength is 3mm~30 μm).Too
With many special materials fully effect, therefore in terms of environmental monitoring, Terahertz is suitable for solid, liquid can occur for hertz
The research of the electricity, acoustic properties of the media such as body, air high-risk chemical and fluid, it can also be used to pollutant monitoring, biology and
The quality control of detection and the food industry of chemical substance.
THz wave has a broadband property, and the frequency band of single terahertz-wave pulse can be covered from several hertz to tens terahertzs
Hereby, detection device can by fourier transform infrared spectroscopy, microwave spectrum, far-infrared laser, non-linear frequency mixing technology,
Far red light grating spectrum and the equally method of energy atmospheric sounding high-risk chemical information, detect detected object.Specifically
, the light source of terahertz time-domain spectroscopy is terahertz pulse of the pulsewidth in picosecond level, and temporal resolution can reach skin
Second；Terahertz time-domain spectroscopy measurement measures for the electric field to terahertz pulse, belongs to coherent measurement, not only includes shaking
The information of width, while the information comprising phase can directly obtain the refractive index of sample；In addition, for some macromolecular air
High-risk chemical, the absworption peak that the spectral line obtained using THz wave is obtained is more sharp, and line style overlapping is less so that big
The discrimination of gas high-risk chemical is more prone to.Particularly, many air high-risk chemicals have uniqueness in THz wave spectral coverage
Absorption line, ingredient, concentration of air high-risk chemical etc. can be measured using terahertz time-domain spectroscopic technology；
Meanwhile terahertz light spectral technology can be used for the absorption for measuring heterogeneity in hybrid atmospheric high-risk chemical, and measure mixed
The chemical composition of air high-risk chemical and the concentration of each component are closed, there is higher accuracy.
Specifically, THz wave has good compared to other detection means in many dielectric materials and nonpolar liquid
Good penetrability, therefore THz wave can carry out perspective imaging to opaque object.Further, since the typical case of Terahertz
Wavelength is much larger than the scale of the soot dust granule in air, these soot dust granules to suspend to the scattering of THz wave much smaller than pair
The scattering of other electromagnetic waves, therefore detection means can be made in more complicated site environment.
Specifically, THz wave has fingerprint spectrality, has absworption peak and the reflection of different frequency to different substances
Peak can efficiently and accurately demarcate the species of air high-risk chemical substance according to the existing finger print information of database；It simultaneously can
The concentration of air high-risk chemical is judged with the feature according to vibration amplitude.Optionally, judged according to the feature of vibration amplitude
The method of air high-risk chemical concentration include the size according to characteristic peak, the peak according to characteristic peak amplitude it
Than be equal to the ratio between air high-risk chemical concentration or and other can reflect that vibration amplitude and air high-risk chemical concentration are closed
The method of system.
Specifically, terahertz emission belongs to the scope of submillimeter wave, and photon energy and characteristic temperature are very low.One frequency
The energy for the photon that rate is 1THz is 4.1MeV, corresponding to 33 wave beams, characteristic temperature 48K, less than various chemical bonds
Bond energy, and the required photon energy of ionized biological tissue will usually reach 16eV, therefore far from making biological tissue or cell
Ionization, therefore harmful ionization reaction will not be caused, suitable for the occasion that explosive is diffused He the crowd is dense.
In one of the embodiments, the terahertz time-domain system is transmission-type terahertz time-domain system.Optionally too
Hertz time domain system is not limited to transmission-type, can also select reflective, differential type, ellipse inclined formula and can atmospheric sounding it is high
Other time domain systems of danger chemicals and high-risk substance probe.
In one of the embodiments, the acquisition methods of target acquisition position include described in step S404：
All concentration distribution information acquired in three-dimensional coordinate are ranked up, obtain concentration highest in three-dimensional coordinate
The direction of point is the direct of travel of the detection device；
The driving detection device marches to the target acquisition position along the direct of travel.
Specifically, the target acquisition position refers to, detection device determines next according to the result of detection of current location
Walk the position that will be detected.Three-dimensional coordinate includes abscissa x, ordinate y and vertical coordinate z.It is described to institute in three-dimensional coordinate
All concentration distribution information obtained are ranked up, and are that all concentration acquired in three-dimensional coordinate are carried out from big to small
Sequence, obtains the coordinate of the point of concentration maximum, i.e. the coordinate (x ', y ', z ') of target acquisition position.
In one of the embodiments, it is described to all concentration distribution information acquired in the three dimensions of current location
Be ranked up, including by Bubble Sort Algorithm to all concentration distribution information acquired in the three dimensions of current location into
Row sequence.
Specifically, it is described according to the air high-risk chemical concentration distribution information acquisition target acquisition position, and drive
Detection device marches to the target acquisition position, including：
S4041 is ranked up all concentration distribution information acquired in the three dimensions of current location, obtains three-dimensional
The direction of peak concentration in space, the direct of travel as the detection device；
S4042 drives the detection device to march to the target acquisition position to the direct of travel.
In one of the embodiments, it is described to all concentration distribution information acquired in the three dimensions of current location
Be ranked up, including by Bubble Sort Algorithm to all concentration distribution information acquired in the three dimensions of current location into
Row sequence.Optionally, the method being ranked up to all concentration distribution information acquired in the three dimensions of current location is unlimited
In bubble sort, simple selection sequence, Straight Insertion Sort, Shell sorting, heapsort, merger sequence, quicksort are further included
And other can realize the algorithm of sequence.
In one of the embodiments, it is described to be visited according to the air high-risk chemical concentration distribution information acquisition target
Location is put, and detection device is driven to march to the target acquisition position and may also include：
S4041 ' to the air high-risk chemical concentration information averaged in the different height of current location, is put down
The highest height of equal concentration is the object height z that detection device is advanced；
S4042 ' is ranked up the concentration of the different angle in the highest height of the mean concentration, obtains described flat
The highest angle of concentration is the target angle of the driving device in the highest height of equal concentration；
S4043 ' drives the detection device to march to the target acquisition according to the object height and target angle
Position.Specifically, the target angle is in a horizontal plane, it is reference with former direction of advance using detection device as origin
(i.e. using the vectorial angle of former direction of advance as 0 °), origin be directed toward the vector of target acquisition position and former direction of advance institute into
Angle.
It in one of the embodiments, can be by multigroup a certain air high-risk chemical distribution in step S408
Concentration information be sent to data handling system and handled.
In one of the embodiments, according to the air high-risk chemical concentration point of the current location in step S408
Cloth information, the air high-risk chemical concentration distribution information of the target acquisition position, output air high-risk chemical space point
The step of cloth image information air high-risk chemical, includes：
S4081 sends the concentration information that multigroup a certain air high-risk chemical is distributed compared with three-dimensional coordinate
Numerical fitting is carried out to numerical fitting system, it is continuously distributed compared with three-dimensional coordinate to obtain a certain air high-risk chemical
Concentration information；
The concentration information continuously distributed compared with three-dimensional coordinate is identified, obtains a certain air by S4082
High-risk chemical spatial distribution map.
In one of the embodiments, in step S4122, by the concentration continuously distributed compared with three-dimensional coordinate
Information carries out colour code, such as area with high mercury is identified with light colour, and low concentration region is represented with dark colour, alternatively, with
Blueness represents a kind of air high-risk chemical, and another air high-risk chemical is represented with red.
Optionally, the concentration information continuously distributed compared with three-dimensional coordinate is not limited to carry out colour code, also
Can carry out words identification, picture identification and other can reflect the identification method of air high-risk chemical concentration information.
In one of the embodiments, the air high-risk chemical concentration distribution information according to the current location,
The air high-risk chemical concentration distribution information of the target acquisition position, obtains air high-risk chemical spatial distribution image
It further includes afterwards：
S4083 respectively detects different types of air high-risk chemical by multiple detection devices, obtains
To the spatial distribution image of a variety of variety classes air high-risk chemicals；
Different types of air high-risk chemical distributed image is overlapped processing, obtained not of the same race by S4084
Class air high-risk chemical spatial distribution superimposed image, and the variety classes air high-risk chemical spatial distribution is superimposed
Image exports.
In one of the embodiments, a kind of computer readable storage medium is also provided, is stored thereon with computer journey
Sequence, wherein, when which is executed by processor, it can be achieved that in any of the above-described embodiment the step of method.
Please refer to fig. 5, a kind of single high-risk chemical source of leaks detection method based on Terahertz, the method
Including：
S502 obtains the air high-risk chemical concentration distribution information of current location by detection device；
S504 according to the air high-risk chemical concentration distribution information acquisition target acquisition position, and drives detection to fill
It puts and marches to the target acquisition position；
S506 obtains the air high-risk chemical concentration distribution information of the target acquisition position, according to the mesh again
The air high-risk chemical concentration distribution information of mark detecting location obtains next target acquisition position, until next target
The air high-risk chemical concentration of detecting location is peak value, reaches S508 at air high-risk chemical source of leaks, is worked as according to described
Air high-risk chemical concentration distribution information, the concentration distribution information of the target acquisition position of front position, obtain air height
Danger chemicals spatial distribution image information.
It is wherein step S502, step S504, step S508 and S402, S404, S408, essentially identical, it is no longer superfluous herein
It states.
Particularly, S506 in one of the embodiments, when the air high-risk chemical of next target acquisition position is dense
Spend for peak value when, reach air high-risk chemical source of leaks at.
The air high-risk chemical source of leaks is the position in a region, can set the phase of the detection of detection device
The distance of adjacent two detecting locations is a step-length.
In one embodiment, when the air high-risk chemical peak concentration point determination methods using the S4041,
During the method for S4042, air high-risk chemical source of leaks is using detection gained air high-risk chemical peak concentration point as origin
Using a step-length as the sphere of radius.
In one embodiment, described in being used when the determination methods of the air high-risk chemical peak concentration point
S4041 ', S4042 ' method when, air high-risk chemical source of leaks is that the gas concentration peak point in corresponding height is origin
Using a step-length as the border circular areas of radius.Optionally, air high-risk chemical leakage source region selection mode be not limited to
Upper two kinds, in varied situations, it can flexibly use multiple choices mode.
Please with reference to Fig. 6, a kind of single air high-risk chemical source of leaks detection method based on Terahertz is described
Method includes：
S602 obtains the air high-risk chemical concentration distribution information and peak value of current location by detection device；
S604 according to the air high-risk chemical concentration distribution information acquisition target acquisition position, and drives detection to fill
It puts and marches to the target acquisition position；
S606 obtains the air high-risk chemical concentration distribution information and peak value of the target acquisition position again, according to
The air high-risk chemical concentration distribution information and peak value of the target acquisition position obtain next target acquisition position, and
Driving detection device marches to next target acquisition position again；
S608, if the magnitude relationship between the peak value of multiple target acquisition positions meets preset condition, according to more
The peak value of a target acquisition position obtains the location information of air high-risk chemical source of leaks；
S610, according to the air high-risk chemical concentration distribution information of the current location, the target acquisition position
Air high-risk chemical concentration distribution information obtains air high-risk chemical spatial distribution image information.
Wherein S602, S604, S606, S610, with S502, S504 in specification, S506, S510, essentially identical, herein
It repeats no more；
Particularly, in one of the embodiments, if magnitude relationship between the peak value of multiple target acquisition positions
Meet preset condition, then the position of air high-risk chemical source of leaks is obtained according to the peak value of multiple target acquisition positions
Information specifically includes：
The air for comparing continuous two target acquisition positions after the current location and the current location is high-risk
The peak value of chemical concentration；
If the peak value of the air high-risk chemical concentration of continuous two target acquisition positions is small after the current location
In the peak value of the air high-risk chemical concentration of the current location, then judge the current location for air high-riskization
Product source of leaks.
In one of the embodiments, if the magnitude relationship between the peak value of multiple target acquisition positions meets in advance
If condition, then the location information for obtaining air high-risk chemical source of leaks according to the peak value of multiple target acquisition positions has
Body further includes：
If the peak value of the air high-risk chemical concentration of the first aim detecting location after the current location is less than
The peak value of the air high-risk chemical concentration of the current location, and the second target detection position after the current location
The air high-risk chemical peak concentration put is more than the air high-risk chemical peak concentration of the current location, then continues to compare
The peak value of the air high-risk chemical concentration of the 3rd target acquisition position after the current location and the present bit
Put the size of air high-risk chemical concentration；
If the peak value of the air high-risk chemical concentration of the 3rd target acquisition position after the current location is less than
The peak value of the air high-risk chemical concentration of the current location, then the current location is that the air high-risk chemical is let out
Drain-source.
Also referring to Fig. 7, a kind of method of multiple high-risk chemicals leakage source detection based on Terahertz, the side
Method includes：
S702 obtains the concentration distribution information of the high-risk chemical of current detecting location by detection device；
S704 draws target acquisition position according to the high-risk chemical concentration distribution information, and driving detection device is advanced
To the target acquisition position；
S706 obtains the concentration distribution information of the target acquisition position again,
Next target acquisition position is obtained according to the high-risk chemical concentration distribution information of the target acquisition position,
When the detection device obtains all source of leaks of a certain high-risk chemical in search coverage, multigroup detecting location is obtained
High-risk chemical concentration distribution information；
The Gas concentration distribution information of multigroup detecting location is sent to data handling system and handled by S708,
Obtain high-risk chemical spatial distribution image information.Wherein S702, S704, S708 and step S602, the S604 in specification,
S608 corresponding steps are essentially identical, and details are not described herein.
Particularly, in one of the embodiments, when air high-risk chemical space exploration imaging method detection obtains
When obtaining all source of leaks of a certain air high-risk chemical in search coverage, the coordinate where the detection device is described
Terminal point coordinate.
In one of the embodiments, judge that the detection device obtains the high-risk chemistry of a certain air in search coverage
The method of all source of leaks of product includes：It is obtained according to the air high-risk chemical concentration distribution information of the target acquisition position
To next target acquisition position, until the coordinate of the coordinate of next target acquisition position and any detecting location before
It overlaps, then judges that the detection device obtains all source of leaks of a certain air high-risk chemical in search coverage.
In one of the embodiments, also referring to Fig. 8, it is described until the coordinate of next target acquisition position with
The coordinate of any detecting location before overlaps, then it is high to judge that the detection device obtains a certain air in search coverage
The method of all source of leaks of danger chemicals includes：
It obtains the coordinate of each target acquisition position and stores in the processing system；
The coordinate of each target acquisition position of the processing system to getting carries out data analysis；
Coordinate when next target acquisition position that processing system detects and the target acquisition position before any one
When the coordinate put overlaps；
Halt instruction is sent to detection device；
The detection device stops detection.
Also referring to Fig. 8, additionally provide in one of the embodiments a kind of based on terahertz detection toxic gas
Method includes：
S802, detection device 100 demarcate gas componant, determine tri- kinds of toxic gases of a, b, c in marked gas；
S804 measures the concentration of toxic gas a；
S8061 adjusts mechanic adjustment unit, the runing rest of connection shaft is made to rotate 0 °, 90 °, 180 °, 270 ° respectively；
S8062 makes telescope support raise 1m, 10m, 20m, 30m height respectively；
S808 measures the concentration data under different coordinates；Concentration data is ranked up by S809, determines detecting devices row
Into direction and height；
If processor sends halt instruction；All concentration datas are carried out numerical fitting by S812 compared with coordinate；S814,
Continuous concentration data is transmitted back to headquarter and is imaged.
If processor does not send halt instruction, repeatedly step S802, S804, S8061, S8062, S808, S809.
The step of repeating S802, S804, S8061, S8062, S808, S809, S810, S812, S814 measures toxic gas
B and c, measure obtain toxic gas b, c concentration distribution information, then the concentration distribution matrix of toxic gas a, b, c is as follows：
By the respective concentration of toxic gas a, b, c according to sorting from big to small, such as a23>a13>a33> a43>…>a22>
a12>a32>A42, it is known that somewhere concentration axyMiddle x represents certain height, and y represents certain angle direction, so that it is determined that 2 → 3 direction of coordinate
For the most fast direction of air high-risk chemical a increasing concen-trations, height 2 is the height of toxic gas a concentration maximums, and coordinate 4 is to have
The height of poisonous gas a concentration minimums；By feeding back electric wire 122, instruction is sent to universal wheel 126, makes universal wheel along increasing concen-trations
Most fast direction, i.e., opposite -135 ° of directions are advanced.All data are collected, by processor 130, by discrete concentration
Numerical fitting is carried out compared with coordinate, so as to obtain gas a, b, c compared with the continuous concentration distribution of three-dimensional coordinate；
Also referring to Fig. 9, Fig. 9 is the concentration result of detection distribution map of poison gas a, by that can be clearly seen than vitta,
Dark color represents low concentration air high-risk chemical, and light color represents high concentration air high-risk chemical, therefore light color aggregation position is
The higher position of poison gas a concentration is judged as the leakage source position of poison gas a, it is proposed that inhibits position for poison gas emphasis.Light color is to deeply
Color extending direction is judged as poison gas a descending concentrations direction, it is proposed that is crowd's escape route；Dark color is sentenced to light extending direction
Break as the concentration sharp increase direction of poison gas a, it is proposed that evade route for crowd's emphasis.
Also referring to Figure 10, situation that Figure 10 a, b two kind poison gas are distributed in space, as seen from the figure, b points of poison gas
Cloth is in high-altitude, and for poison gas a in low latitude, situations such as this density and same day wind-force to gas in itself is related.According to different types of gas
The sprinkling of corresponding chemical treatment medicament can be effectively performed in the space distribution situation of body.Since low latitude poison gas is to people's
Life security influence is big compared with high-altitude poison gas, and judges that poison gas a concentration is big compared with poison gas b, therefore Ying You from shade
First handle the leakage of poison gas a.
It can be with the leakage situation of accurate judgement poison gas a and poison gas b, so as to help by intuitively showing for Fig. 9 and Figure 10
Poison gas Restrain measurement and crowd evacuation scheme are made in commanding.
Each technical characteristic of embodiment described above can be combined arbitrarily, to make description succinct, not to above-mentioned reality
It applies all possible combination of each technical characteristic in example to be all described, as long as however, the combination of these technical characteristics is not deposited
In contradiction, the scope that this specification is recorded all is considered to be.
Embodiment described above only expresses the several embodiments of the present invention, and description is more specific and detailed, but simultaneously
Cannot the limitation to the scope of the claims of the present invention therefore be interpreted as.It should be pointed out that for those of ordinary skill in the art
For, without departing from the inventive concept of the premise, various modifications and improvements can be made, these belong to the present invention's
Protection domain.Therefore, the protection domain of patent of the present invention should be determined by the appended claims.
Claims (10)
- A kind of 1. method based on the distribution of terahertz detection high-risk chemical, which is characterized in that the described method includes：The concentration distribution information of the air high-risk chemical of current detecting location is obtained by detection device；According to the air high-risk chemical concentration distribution acquisition of information target acquisition position, driving detection device marches to described Target acquisition position；The air high-risk chemical concentration distribution information of the target acquisition position is obtained again；Next target acquisition position is obtained according to the air high-risk chemical concentration distribution information of the target acquisition position, directly Coordinate to next target acquisition position is overlapped with the coordinate of any detecting location before, obtains the big of multigroup detecting location Gas high-risk chemical concentration distribution information；The Gas concentration distribution information of multigroup detecting location is sent to data handling system to handle, obtains air height Danger chemicals spatial distribution image information.
- 2. according to the method described in claim 1, it is characterized in that, the detection device is terahertz time-domain system.
- 3. according to the method described in claim 2, it is characterized in that, the terahertz time-domain system is transmission-type terahertz time-domain System.
- 4. according to the method described in claim 1, it is characterized in that, the acquisition methods of next target acquisition position include：All concentration distribution information acquired in three-dimensional coordinate are ranked up, obtain the side of concentration peak in three-dimensional coordinate To the direct of travel for the driving device；The driving device marches to next target acquisition position along the direct of travel.
- 5. according to the method described in claim 4, it is characterized in that, described own to acquired in the three dimensions of current location Concentration distribution information is ranked up, including by Bubble Sort Algorithm to all concentration acquired in the three dimensions of current location Distributed intelligence is ranked up.
- 6. according to the method described in claim 1, it is characterized in that, described believe according to the air high-risk chemical concentration distribution Breath obtains target acquisition position, and detection device is driven to march to the target acquisition position and is further included：To the concentration information averaged in the different height of current location, it is high for target to obtain the highest height of mean concentration Degree；The concentration of different angle in the highest height of the mean concentration is ranked up, it is highest to obtain the mean concentration The highest angle of concentration is the target angle of the driving device in height；The detection device is driven to march to the target acquisition position according to the object height and target angle.
- 7. according to the method described in claim 1, it is characterized in that, by multigroup a certain air high-risk chemical distribution Concentration information is sent to data handling system and is handled, and the step of obtaining air high-risk chemical spatial distribution image information wraps It includes：Multigroup a certain air high-risk chemical is sent to numerical fitting compared with the concentration information that three-dimensional coordinate is distributed System carries out numerical fitting, obtains a certain air high-risk chemical compared with the continuously distributed concentration information of three-dimensional coordinate；The concentration information continuously distributed compared with three-dimensional coordinate is identified, it is empty to obtain a certain air high-risk chemical Between distribution map.
- 8. the according to the method described in claim 5, it is characterized in that, air high-risk chemical according to the current location Concentration distribution information, the air high-risk chemical concentration distribution information of the target acquisition position, obtain air high-risk chemical It is further included after spatial distribution image：Different types of air high-risk chemical is detected respectively by multiple detection devices, is obtained a variety of not of the same race The gas compartment distributed image of class gas；Different types of air high-risk chemical distributed image is overlapped processing, obtains variety classes air high-riskization Product spatial distribution superimposed image, and the variety classes air high-risk chemical spatial distribution superimposed image is exported.
- 9. according to the method described in claim 5, it is characterized in that, the concentration continuously distributed compared with three-dimensional coordinate is believed Breath carries out colour code.
- 10. a kind of computer readable storage medium, is stored thereon with computer program, which is characterized in that the program is by processor The step of any one the method in claim 1-9 can be realized during execution.
Priority Applications (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201711329777.2A CN108107017B (en) | 2017-12-13 | 2017-12-13 | Method based on the distribution of terahertz detection high-risk chemical |
| PCT/CN2018/092436 WO2019114239A1 (en) | 2017-12-13 | 2018-06-22 | Terahertz detection method and system for highly hazardous chemical in atmosphere |
| US16/446,620 US20190302012A1 (en) | 2017-12-13 | 2019-06-20 | Terahertz detection method and system for high-risk chemical in atmosphere |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201711329777.2A CN108107017B (en) | 2017-12-13 | 2017-12-13 | Method based on the distribution of terahertz detection high-risk chemical |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN108107017A true CN108107017A (en) | 2018-06-01 |
| CN108107017B CN108107017B (en) | 2019-05-17 |
Family
ID=62215844
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201711329777.2A Active CN108107017B (en) | 2017-12-13 | 2017-12-13 | Method based on the distribution of terahertz detection high-risk chemical |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN108107017B (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109781656A (en) * | 2018-12-27 | 2019-05-21 | 深圳市华讯方舟太赫兹科技有限公司 | Vapor detection system and detection method based on Terahertz |
| CN111351764A (en) * | 2020-02-27 | 2020-06-30 | 云南电网有限责任公司电力科学研究院 | Material detection device and detection method based on terahertz technology |
| CN115855586A (en) * | 2022-12-20 | 2023-03-28 | 山东诺方电子科技有限公司 | Multi-point atmospheric sampler and sampling method |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103575675A (en) * | 2013-10-30 | 2014-02-12 | 中国科学院安徽光学精密机械研究所 | Onboard multi-angle region pollution distribution scanning detection device |
| US20140353531A1 (en) * | 2013-05-30 | 2014-12-04 | Stephen T. Hanley | System and method of retrieving mass density distributions and thermal profiles from the atmosphere to identify molecular constituents that may absorb spectral energy |
| CN104280789A (en) * | 2014-10-29 | 2015-01-14 | 清华大学 | Locating method, locating device, treatment device and system for chemical leakage source |
| CN105300912A (en) * | 2015-09-16 | 2016-02-03 | 上海安允科技有限公司 | System for monitoring a variety of dangerous gases based on absorption spectrum remote sensing technology |
| CN106338484A (en) * | 2015-07-09 | 2017-01-18 | 王霆 | Apparatus for monitoring environment gas information by unmanned plane infrared remote sensing and application thereof |
-
2017
- 2017-12-13 CN CN201711329777.2A patent/CN108107017B/en active Active
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20140353531A1 (en) * | 2013-05-30 | 2014-12-04 | Stephen T. Hanley | System and method of retrieving mass density distributions and thermal profiles from the atmosphere to identify molecular constituents that may absorb spectral energy |
| CN103575675A (en) * | 2013-10-30 | 2014-02-12 | 中国科学院安徽光学精密机械研究所 | Onboard multi-angle region pollution distribution scanning detection device |
| CN104280789A (en) * | 2014-10-29 | 2015-01-14 | 清华大学 | Locating method, locating device, treatment device and system for chemical leakage source |
| CN106338484A (en) * | 2015-07-09 | 2017-01-18 | 王霆 | Apparatus for monitoring environment gas information by unmanned plane infrared remote sensing and application thereof |
| CN105300912A (en) * | 2015-09-16 | 2016-02-03 | 上海安允科技有限公司 | System for monitoring a variety of dangerous gases based on absorption spectrum remote sensing technology |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109781656A (en) * | 2018-12-27 | 2019-05-21 | 深圳市华讯方舟太赫兹科技有限公司 | Vapor detection system and detection method based on Terahertz |
| CN111351764A (en) * | 2020-02-27 | 2020-06-30 | 云南电网有限责任公司电力科学研究院 | Material detection device and detection method based on terahertz technology |
| CN111351764B (en) * | 2020-02-27 | 2024-01-23 | 云南电网有限责任公司电力科学研究院 | Material detection device and method based on terahertz technology |
| CN115855586A (en) * | 2022-12-20 | 2023-03-28 | 山东诺方电子科技有限公司 | Multi-point atmospheric sampler and sampling method |
| CN115855586B (en) * | 2022-12-20 | 2023-08-11 | 山东诺方电子科技有限公司 | Multi-point atmospheric sampler and sampling method |
Also Published As
| Publication number | Publication date |
|---|---|
| CN108107017B (en) | 2019-05-17 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN108107017B (en) | Method based on the distribution of terahertz detection high-risk chemical | |
| US20190302012A1 (en) | Terahertz detection method and system for high-risk chemical in atmosphere | |
| CN106769974B (en) | Gas concentration Two dimensional Distribution on-line detecting system and method | |
| Neumann et al. | Aerial-based gas tomography–from single beams to complex gas distributions | |
| Di Martino et al. | Spatial domain analysis of carbon dioxide from soils on Vulcano Island: Implications for CO2 output evaluation | |
| CN108121777B (en) | The method of multiple high-risk chemicals leakage source detection based on Terahertz | |
| Trincavelli et al. | A Least Squares approach for learning gas distribution maps from a set of integral gas concentration measurements obtained with a TDLAS sensor | |
| CN107843573A (en) | The reflexive feedback system of Terahertz of air high-risk chemical detection | |
| CN110470615A (en) | A kind of chemical gas concentration monitoring method and system | |
| CN108169160B (en) | Single atmosphere high-risk chemical source of leaks detection method based on Terahertz | |
| CN207742107U (en) | The reflexive feedback system of Terahertz of air high-risk chemical detection | |
| CN207610987U (en) | Terahertz detection air high-risk chemical distribution apparatus | |
| Gondal et al. | Laser Doppler velocimeter for remote measurement of polluted water and aerosols discharges | |
| Yang et al. | Simultaneous detection of multiple gaseous pollutants using multi-wavelength differential absorption LIDAR | |
| Gaudio et al. | Lidar and Dial application for detection and identification: a proposal to improve safety and security | |
| CN108169159B (en) | Atmosphere high-risk chemical spatial distribution judgment method based on Terahertz | |
| CN207675651U (en) | Portable underwater deposit, rock composition detection device based on LIBS technologies | |
| CN108828050A (en) | A kind of poison gas intelligent monitor system and monitoring method | |
| Reiche et al. | Comparative study to evaluate three ground-based optical remote sensing techniques under field conditions by a gas tracer experiment | |
| RU114532U1 (en) | SPECTRADO-RADIOMETRIC INSTALLATION OF REMOTE GAS CONTROL OF THE WORKING ZONE OF CHEMICALLY DANGEROUS OBJECTS BY STRONG NUCLEAR POISON SUBSTANCES | |
| Puiu et al. | Lidar/DIAL detection of acetone at 3.3 μm by a tunable OPO laser system | |
| CN111352170B (en) | Sectional scanning method | |
| Pasqualino et al. | Application of optical techniques to detect chemical and biological agents | |
| Kouichi et al. | Optimization of sensor networks for the estimation of atmospheric pollutants sources | |
| Dobler et al. | Greenhouse Gas Laser Imaging Tomography Experiment (GreenLITE) |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant |