CN103234882B - A kind of Atmospheric particulates mass concentration inversion method based on the particulate matter flight time - Google Patents
A kind of Atmospheric particulates mass concentration inversion method based on the particulate matter flight time Download PDFInfo
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Abstract
A kind of Atmospheric particulates mass concentration inversion method based on the particulate matter flight time, can be finally inversed by the mass concentration of particulate matter on the basis of aerodynamic grain spectrometer according to flight speed and sampling flow.According to the operation principle of aerodynamic grain spectrometer, after granule is by accelerating spout, any point on air trajectory, the particulate matter of every kind of particle diameter has unique speed up, the flight speed of particle can be drawn by the flight time.Flight speed and the relationship between quality of particle can be drawn by principle of conservation of momentum, aerodynamic and fluid mechanics principle, therefore can be finally inversed by the mass concentration of particulate matter by flight speed and sampling flow.The present invention is finally inversed by the mass concentration of Atmospheric particulates according to the dynamic characteristic of particulate matter;There is provided a kind of energy accurately, in real time, the inversion algorithm of on-line measurement Atmospheric particulates mass concentration.
Description
Technical field
The present invention relates to Atmospheric particulates mass concentration method for real-time measurement, belong to atmosphere environment supervision technical field.
Background technology
In recent years, along with the haze weather in the particularly flourishing city of China's most area and area frequently occurs, people are to air
Quality is increasingly paid attention to.The main cause forming haze weather is that atmosphere particle concentration rises, particularly PM2.5 concentration upper
Rise, cause air quality to deteriorate and visibility drastically descends degradation adverse effect.The size of particulate matter and human body in haze weather
Health has close relationship, and it determines that it eventually enters into the position of respiratory tract and deposition.Poisonous, harmful in haze weather
Particulate matter disseminates in atmosphere, and the mankind and ecosystem can be caused harm in various degree.Currently, the detection of Atmospheric particulates
Become the important content in the fields such as environment, weather and health.
At present, the main measurement method of atmosphere particle monitoring has: oscillating balance method, Beta ray method, light scattering method.Vibration
Sedimentation balance method can directly measure the concentration of particulate matter, unrelated with particle size, color etc., but its by sample temperature, humidity,
The impact such as vibration, noise is bigger, and particularly in sampling process, in Atmospheric particulates, volatile organic matter loss causes measurement error
Bigger.Beta ray method is unrelated with the kind of particulate matter, particle diameter, shape, color and chemical composition etc., only with the quality of particle
Relevant, but affected the biggest by radiographic source, filter paper individuality difference.It addition, oscillating balance method and Beta ray method will coordinate PM10,
The sicklies such as PM2.5, owing to the error of sickle will also result in measuring result error.Further, oscillating balance method and Beta ray
Method cannot provide Particle density and the particle diameter distributed intelligence of each particle diameter of Atmospheric particulates, and the two parameter is all to affect health
One of important parameter.Light scattering method is that the intensity size of the scattered light signal by sending after measuring the irradiation of particulate matter light is measured
The mass concentration of particulate matter.At present, Atmospheric particulates calculating instrument based on light scattering method is more, such as Grimm company of Germany
1.109, the 3413 of 3330 and the Metone company of the U.S. of Technical Sourcing Internation of the U.S. etc..Light scattering method surveys the mass concentration of particulate matter
Mainly measure particulate matter optics particle diameter by the scattered light intensity size of special angle, and the quality of further inverting particulate matter is dense
Degree, the fluctuation of laser instrument light intensity, particle refractive index and geometry the most all can cause measurement error.
Summary of the invention
The technology of the present invention solves problem: overcome the deficiency of above-mentioned problem, it is provided that a kind of air based on the particulate matter flight time
Grain material amount retrieving concentration method, can realize accurately, in real time, online, can continuous print Atmospheric particulates mass concentration monitor, energy
Measure the mass concentration of PM10, PM2.5, PM1 simultaneously, and provide grain-size of atmospheric particulate substance distribution.
The technology implementation scheme of the present invention: on the basis of aerodynamic size spectrometer, a kind of based on the particulate matter flight time
Atmospheric particulates mass concentration inversion method, it is achieved step is as follows:
(1) particulate matter flight time at double hot spots can, by aerodynamic size spectrometer be measured, according to the distance of double hot spots
L calculates the flight speed of particle, and formula is as follows:
Wherein: v is the flight speed of particulate matter, L is the distance of double hot spot, and △ t is the particulate matter flight time at double hot spots.
The flight speed of particulate matter can be drawn by the flight time, draw the quality of particulate matter according to flight speed.
(2), flying speed of partcles and single grain can be drawn according to the law of conservation of momentum, aerodynamic and fluid mechanics principle
The relational expression of the quality of son, formula is as follows:
Wherein: dmdBeing the quality of a certain particle diameter single particle, v is the flight speed of particulate matter, C1For systematic features coefficient,
C2For particulate matter flight speed correction factor, C3For the speed of gas, C4For the correction factor of gas velocity,L is speed
Degree measures point and jet opening distance, and Z is Particles transport rate.Show that the quality of a certain particle diameter single particle can this particle diameter of root
The accumulated gross mass calculating this particles thing of the number of particulate matter.
(3), according to the particle diameter sum concentration information of particulate matter, calculating the gross mass of a certain particles thing, computing formula is such as
Under:
In formula, N be particle size be the total number of particles of d, dmdBe particle size be the quality of the single particle of d,
mdBe particle diameter be the quality of all particulates corresponding to d.After drawing the gross mass of a certain particles thing, according to the model of particle diameter
Enclose and calculate the particulate matter gross mass that all particle diameters are corresponding, all particle diameter correspondence particulate matter gross masses are added in drawing particle size range
Particulate matter gross mass, draw the mass concentration of surveyed particulate matter finally according to the flow used and time.
(4), by the scope of grain-size of atmospheric particulate substance, the quality of Atmospheric particulates is calculated according to the flow sampled and sampling time
Concentration, computing formula is as follows:
In formula, D is the maximum particle diameter of the measured Atmospheric particulates arrived, and L is sampling flow, and t is the sampling time, and PM is big
The mass concentration of aerated particle thing.
(5), standard aerosol particle generator is used to produce standard particle thing.Standard aerosol particle generator aperture selects
20 μm, utilize DOP solution to produce the standard particle thing of 20 groups of different solutions concentration.
(6) aerodynamic grain spectrometer, is utilized to measure the standard particle of the 20 groups of different solutions concentration obtained in step (5)
The flight time of thing, the flight time calculate flight speed according to formula (6).Calculate the mark of 20 groups of different solutions concentration
The quality of quasi-particulate matter, mass particle is calculated by following formula:
In formula, ρ is the mass particle density of DOP;DdIt it is liquid-drop diameter.
DdCan be obtained by following formula:
In formula, Q is liquid supply rate, i.e. flow rate of liquid, and f is frequency of vibration, and C is volumetric concentration.
(7), quality and the flight speed of the standard particle thing produced under the 20 groups of different solutions concentration obtained in step (6)
Data are fitted, and use 5 order polynomial matchings:
Y=A+B1x1+B2x2+B3x3+B4x4+B5x5 (5)
Wherein, y is the inverse of the quality of single particle, and x is the flight time of particulate matter, A, B1、B2、B3、B4、
B5It is 5 order polynomial fitting parameters, uses method of least square to obtain parameter A, B after carrying out linear fit1、B2、B3、B4、
B5, and draw the matched curve of correspondence.Fractional part is launched by Taylor's formula in formula (1), according to matching out
Curve finally determines C in formula (1)1、C2、C3、C4, k.Formula (1) fractional part is launched by Taylor's formula
Formula is as follows:
In formula: dmdBeing the quality of a certain particle diameter single particle, v is the flight speed of particulate matter, C1For systematic features
Coefficient, C2For particulate matter flight speed correction factor, C3For the speed of gas, C4For the correction factor of gas velocity,L
For tachometric survey point and jet opening distance, Z is Particles transport rate.
Compared with measuring technology with existing Atmospheric particulates mass concentration, it is an advantage of the current invention that:
(1) present invention combines light scattering and time-of-flight carrys out inverting Atmospheric particulates mass concentration, is avoided that by particulate matter
The error that refractive index is different with geometry and causes, thus improve the inversion accuracy of Atmospheric particulates mass concentration.
(2) parameter that matching of the present invention obtains is used, it is not necessary to measure the systematic parameters such as double hot spot distances and i.e. can realize particulate matter
The accurate calibration of particle diameter.
(3) present invention realizes the fast inversion of Atmospheric particulates PM10, PM2.5, PM1.
(4) the particulate matter quality retrieving concentration in the present invention is to be obtained by the measurement flight time, and laser instrument light-intensity variation can be drawn
Play scattered light intensity change, but flight time measurement result will not be produced impact, thus reduce quick to environmental change of measurement result
Perception.
Accompanying drawing explanation
Fig. 1 is the flowchart of the inventive method.
Detailed description of the invention
As it is shown in figure 1, present invention Atmospheric particulates based on particulate matter flight time mass concentration inversion algorithm specifically comprises the following steps that
The first step, the particle flight time at double hot spots can be measured by aerodynamic size spectrometer, according to the distance of double hot spots
L calculates the flight speed of particle, and formula is as follows:
Wherein: v is the flight speed of particulate matter, L is the distance of double hot spot, and △ t is the particulate matter flight time at double hot spots.
The flight speed of particulate matter can be drawn by the flight time, draw the quality of particulate matter according to flight speed.
After second step, granule are by accelerating spout, any point on air trajectory, the particulate matter of every kind of particle diameter has uniquely
Speed up.According to momentum theorem, in particulate matter, the differential momentum conservation equation of each particulate matter can use formula (7)
Represent:
Wherein, subscript p represents particulate matter;For gas molecule collision to the mean force of particulate matter;Subscript
G represents and carries gas;Z is Particles transport rate;mpG is the gravity of particulate matter self.
Because for gas molecule collision is to the mean force of particulate matter, the gravity of particulate matter itself is the least, i.e. gravity accelerates
Spend the least relative to the acceleration that gas molecule collision brings, during calculating, the impact of gravity can be ignored.Formula (9)
It is reduced to:
Because double facula positions distance spout is close, for the ease of calculating, it is believed that Z and ugFor constant.Finally draw particle flight
The relational expression of the quality of speed and single particle, formula is as follows:
In formula: dmdBeing the quality of a certain particle diameter single particle, v is the flight speed of particulate matter, C1For systematic features coefficient,
C2For particulate matter flight speed correction factor, C3For the speed of gas, C4For the correction factor of gas velocity,L is
Tachometric survey point and jet opening distance, Z is Particles transport rate.Show that the quality of a certain particle diameter single particle can this grain of root
The accumulated gross mass calculating this particles thing of the number of footpath particulate matter.
3rd step, particle diameter sum concentration information according to particulate matter, calculate the gross mass of a certain particles thing, computing formula
As follows:
In formula, N be particle size be the total number of particles of d, dmdBe particle size be the quality of the single particle of d, md
Be particle diameter be the quality of all particles corresponding to d.After drawing the gross mass of a certain particles thing, according to the range computation of particle diameter
Go out the particulate matter gross mass that all particle diameters are corresponding, the addition of all particle diameter correspondence particulate matter gross masses is drawn the granule in particle size range
Thing gross mass, draws the mass concentration of surveyed particulate matter finally according to the flow used and time.
4th step, by the scope of grain-size of atmospheric particulate substance, calculate the matter of Atmospheric particulates according to the flow of sampling and sampling time
Amount concentration, computing formula is as follows:
In formula, D is the maximum particle diameter of Atmospheric particulates, and L is sampling flow, and t is the sampling time, and PM is Atmospheric particulates
Mass concentration.
5th step, employing standard aerosol particle generator produce standard particle thing.Aperture selects 20 μm, utilizes DOP solution
Produce the standard particle thing of 20 groups of different solutions concentration.
6th step, utilize the standard of 20 groups of different solutions concentration that aerodynamic grain spectrometer obtains in measuring described in the 5th step
The flight time of particulate matter, the flight time calculate flight speed according to formula (6).Calculate 20 groups of different solutions concentration
The quality of standard particle thing, mass particle is calculated by following formula:
In formula, ρ is the mass particle density of DOP;DdIt it is liquid-drop diameter.
DdCan be obtained by following formula:
In formula, Q is liquid supply rate, i.e. flow rate of liquid, and f is frequency of vibration, and C is volumetric concentration.
The quality of the standard particle thing produced under the 7th step, 20 groups of different solutions concentration that the 6th step is drawn and flight speed number
According to being fitted, use 5 order polynomial matchings:
Y=A+B1x1+B2x2+B3x3+B4x4+B5x5 (5)
Wherein, y is the inverse of the quality of single particle, and x is the flight time of particulate matter, A, B1、B2、B3、B4、
B5It is 5 order polynomial fitting parameters, uses method of least square to obtain parameter A, B after carrying out linear fit1、B2、B3、B4、
B5, and draw corresponding matched curve, fractional part being launched by Taylor's formula in formula (1), obtain formula (9),
C in formula (1) is finally determined according to matching parameter out1、C2、C3、C4, k.
In formula: dmdBeing the quality of a certain particle diameter single particle, v is the flight speed of particulate matter, C1For systematic features coefficient,
C2For particulate matter flight speed correction factor, C3For the speed of gas, C4For the correction factor of gas velocity,L is speed
Degree measures point and jet opening distance, and Z is Particles transport rate.
Y=A+B1x1+B2x2+B3x3+B4x4+B5x5The physical meaning of all symbols of formula;
The Atmospheric particulates flight time that 8th step, basis record, the flight time is converted into flight speed, finally by calculating
Machine is finally inversed by the mass concentration of Atmospheric particulates through above-mentioned steps.
Non-elaborated part of the present invention belongs to techniques well known.
The above, part detailed description of the invention the most of the present invention, but protection scope of the present invention is not limited thereto, and any ripe
Know those skilled in the art in the technical scope that the invention discloses, the change that can readily occur in or replacement, all should contain in the present invention
Protection domain within.
Claims (1)
1. an Atmospheric particulates mass concentration inversion method based on the particulate matter flight time, it is characterised in that realize step such as
Under:
(1), by aerodynamic size spectrometer measure the particulate matter flight time at double hot spots, count according to distance L of double hot spots
Calculating the flight speed of particle, formula is as follows:
Wherein: v is the flight speed of particulate matter, L is the distance of double hot spot, and Δ t is the particulate matter flight time at double hot spots;
(2) flight speed of particulate matter, by the flight time is drawn, according to the law of conservation of momentum, aerodynamic and hydrodynamics
Principle draws the relational expression of flying speed of partcles and the quality of single particle, draws the quality of particulate matter, and formula is as follows:
Wherein: dmdBeing the quality of a certain particle diameter single particle, v is the flight speed of particulate matter, C1For systematic features coefficient,
C2For particulate matter flight speed correction factor, C3For the speed of gas, C4For the correction factor of gas velocity,L is
Tachometric survey point and jet opening distance, Z is Particles transport rate;
(3) utilize the quality of a certain particle diameter single particle, calculate this grain according to the number of this particles thing is accumulated
The gross mass of footpath particulate matter,
Computing formula is as follows:
In formula, N be particle size be the total number of particles of d, dmdBe particle size be the quality of the single particle of d,
mdBe particle diameter be the quality of all particulates corresponding to d;
(4) by the scope of grain-size of atmospheric particulate substance, the quality of Atmospheric particulates is calculated according to the flow sampled and sampling time
Concentration, computing formula is as follows:
In formula, D is the maximum particle diameter of the measured Atmospheric particulates arrived, and L is sampling flow, and t is the sampling time, and PM is big
The mass concentration of aerated particle thing;
(5), using standard aerosol particle generator to produce standard particle thing, standard aerosol particle generator aperture selects
20 μm, utilize DOP solution to produce the standard particle thing of 20 groups of different solutions concentration;
(6) aerodynamic grain spectrometer, is utilized to measure the standard particle of the 20 groups of different solutions concentration obtained in step (5)
The flight time of thing, the flight time calculate flight speed according to formula (6), calculate the mark of 20 groups of different solutions concentration
The quality of quasi-particulate matter, mass particle is calculated by following formula:
In formula, ρ is the mass particle density of DOP;DdIt is liquid-drop diameter,
DdCan be obtained by following formula:
In formula, Q is liquid supply rate, i.e. flow rate of liquid, and f is frequency of vibration, and C is volumetric concentration;
(7), quality and the flight speed of the standard particle thing produced under the 20 groups of different solutions concentration obtained in step (5)
Data are fitted, and use 5 order polynomial matchings:
Y=A+B1x1+B2x2+B3x3+B4x4+B5x5 (5)
Wherein, y is the inverse of the quality of single particle, and x is the flight time of particulate matter, A, B1、B2、B3、B4、
B5It is 5 order polynomial fitting parameters, uses method of least square to obtain parameter A, B after carrying out linear fit1、B2、B3、B4、
B5, and draw the matched curve of correspondence, in formula (1) to fractional part by Taylor's formula expansion, according to matching out
Curve finally determines C in formula (1)1、C2、C3、C4, k, formula (1) to fractional part by Taylor's formula launch
Formula is as follows:
In formula: dmdBeing the quality of a certain particle diameter single particle, v is the flight speed of particulate matter, C1For systematic features
Coefficient, C2For particulate matter flight speed correction factor, C3For the speed of gas, C4For the correction factor of gas velocity,
L is tachometric survey point and jet opening distance, and Z is Particles transport rate;
(8), according to the Atmospheric particulates flight time recorded, the flight time is converted into flight speed, finally by computer
The mass concentration of Atmospheric particulates it is finally inversed by through above-mentioned steps.
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CN106018194A (en) * | 2016-05-18 | 2016-10-12 | 深圳市青核桃科技有限公司 | Method using laser particle counting machine to calculate particle mass |
CN108120661B (en) * | 2017-12-19 | 2021-02-05 | 北京理工大学 | Method for measuring space-time distribution of particulate matter content in urban air |
CN108709836B (en) * | 2018-07-26 | 2024-03-19 | 宁夏大学 | Aerosol detection method and system |
CN109632589B (en) * | 2018-12-30 | 2024-03-12 | 江苏苏净集团有限公司 | Atmospheric particulate detection device and method |
CN109738345B (en) * | 2019-01-17 | 2021-08-20 | 中国科学院城市环境研究所 | Real-time quantitative analysis method for single-particle aerosol |
CN114112817A (en) * | 2021-11-30 | 2022-03-01 | 中国科学院合肥物质科学研究院 | Particle size spectrum inversion correction method for eliminating multi-charge effect of particulate matters |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5949001A (en) * | 1998-02-17 | 1999-09-07 | Willeke; Klaus | Method for aerodynamic particle size analysis |
CN102608004A (en) * | 2012-03-14 | 2012-07-25 | 北京汇丰隆生物科技发展有限公司 | Aerodynamic size spectrometer |
-
2013
- 2013-04-21 CN CN201310139285.2A patent/CN103234882B/en active Active
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5949001A (en) * | 1998-02-17 | 1999-09-07 | Willeke; Klaus | Method for aerodynamic particle size analysis |
CN102608004A (en) * | 2012-03-14 | 2012-07-25 | 北京汇丰隆生物科技发展有限公司 | Aerodynamic size spectrometer |
Non-Patent Citations (2)
Title |
---|
《THEORETICAL BASIS OF THE TIME-OF-FLIGHT AEROSOL SPECTROMETER: A METHOD FOR MONITORING THE SIZE DISTRIBUTION OF SUBMICRON AEROSOL PARTICLES》;MICHAEL H. SCHWARTZ;《Journal of Aerosol Science>;19761231;第7卷;第281-296页 * |
邢建永.《空气动力学粒谱分析仪标定方法研究》.《大气与环境光学学报》.2007,第2卷(第3期),第211-213页. * |
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