CN103234882A - Method for inverting mass concentration of atmospheric particulates based on flight time of particulates - Google Patents

Method for inverting mass concentration of atmospheric particulates based on flight time of particulates Download PDF

Info

Publication number
CN103234882A
CN103234882A CN2013101392852A CN201310139285A CN103234882A CN 103234882 A CN103234882 A CN 103234882A CN 2013101392852 A CN2013101392852 A CN 2013101392852A CN 201310139285 A CN201310139285 A CN 201310139285A CN 103234882 A CN103234882 A CN 103234882A
Authority
CN
China
Prior art keywords
particle
formula
particle diameter
particulates
quality
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
Application number
CN2013101392852A
Other languages
Chinese (zh)
Other versions
CN103234882B (en
Inventor
桂华侨
李德平
刘建国
程寅
王杰
陆亦怀
伍德侠
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Hefei Institutes of Physical Science of CAS
Original Assignee
Hefei Institutes of Physical Science of CAS
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Hefei Institutes of Physical Science of CAS filed Critical Hefei Institutes of Physical Science of CAS
Priority to CN201310139285.2A priority Critical patent/CN103234882B/en
Publication of CN103234882A publication Critical patent/CN103234882A/en
Application granted granted Critical
Publication of CN103234882B publication Critical patent/CN103234882B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Abstract

The invention relates to a method for inverting the mass concentration of atmospheric particulates based on the flight time of the particulates. The mass concentration of the particulates can be inverted according to the flight speed and the sampling flow on the basis of an aerodynamic particulate spectrometer. According to the work principle of the aerodynamic particulate spectrometer, the particulates with different particle sizes have only speed up at any one point on an airflow track after the particulates pass through an accelerating nozzle, so the flight speed of particles can be obtained through the flight time. The relationship between the flight speed and the mass of the particles can be obtained according to a momentum conservation theorem and aerodynamic and hydromechanical principles, so the mass concentration of the particulates can be inverted through the flight speed and the sampling flow. The method provided by the invention can be used for inverting the mass concentration of the atmospheric particulates according to the dynamic feature of the particulates and provides an inversion algorithm capable of measuring the mass concentration of the atmospheric particulates accurately, in real time and on line.

Description

A kind of Atmospheric particulates mass concentration inversion method based on the particle flight time
Technical field
The present invention relates to Atmospheric particulates mass concentration method for real-time measurement, belong to the atmosphere environment supervision technical field.
Background technology
In recent years, along with the most of area of China particularly frequently occurs with regional haze weather in flourishing city, people more and more pay attention to air quality.The main cause that forms grey haze weather is that atmosphere particle concentration rises, and the particularly rising of PM2.5 concentration causes that air quality worsens and visibility is sharply descended the degradation adverse effect.Particle size and the health of particle have close relationship in the ash haze weather, and it determines position and the deposition that it finally enters respiratory tract.Poisonous, deleterious particle thing in the ash haze weather are spread out in the air, can cause in various degree harm to human and the ecosystem.Current, the detection of Atmospheric particulates has become the important content in fields such as environment, weather and health.
At present, the main measuring method of atmosphere particle monitoring has: vibration sedimentation balance method, Beta rays method, light scattering method.The vibration sedimentation balance method can directly be measured the concentration of particle, irrelevant with particle particle diameter, color etc., it is bigger that but it is influenced by sample temperature, humidity, vibration, noise etc., particularly in the sampling process in the Atmospheric particulates volatile organic matter loss cause that measuring error is bigger.The kind of Beta rays method and particle, particle diameter, shape, color and chemical composition etc. are irrelevant, and are only relevant with the quality of particle, but are subjected to radiographic source, the individual differences affects of filter paper very big.In addition, vibration sedimentation balance method and Beta rays method all will cooperate cutters such as PM10, PM2.5, because the error of cutter also can cause measuring result error.And vibration sedimentation balance method and Beta rays method can't provide several concentration and the particle diameter distributed intelligence of each particle diameter of Atmospheric particulates, and these two parameters all are one of important parameters that influences health.Light scattering method is the mass concentration of measuring particle by the intensity size of measuring the scattered light signal that sends after particle is penetrated by illumination.At present, more based on the Atmospheric particulates calculating instrument of light scattering method, as German Grimm company 1.109,3330 and the U.S. Metone company of U.S. Technical Sourcing Internation 3413 etc.The mass concentration that light scattering method is surveyed particle mainly is to measure particle optics particle diameter by the scattered light intensity size of special angle, and the mass concentration of further inverting particle, the different of the fluctuation of laser instrument light intensity, the refractive index of particle and geometric configuration all can cause measuring error.
Summary of the invention
The technology of the present invention is dealt with problems: the deficiency that overcomes above-mentioned problem, a kind of Atmospheric particulates mass concentration inversion method based on the particle flight time is provided, can realize accurate, real-time, online, continuable Atmospheric particulates mass concentration monitoring, can measure the mass concentration of PM10, PM2.5, PM1 simultaneously, and provide the distribution of Atmospheric particulates particle diameter.
Implementer's case of the present invention: on the basis of aerodynamic size spectrometer, a kind of Atmospheric particulates mass concentration inversion method based on the particle flight time, performing step is as follows:
(1), can measure particle in the flight time of two hot spots by the aerodynamic size spectrometer, calculate the flying speed of particle according to the distance L of two hot spots, formula is as follows:
v = L Δt - - - ( 7 )
Wherein: v is the flying speed of particle, and L is the distance of two hot spots, and Δ t is that particle is in the flight time of two hot spots.Can draw the flying speed of particle by the flight time, draw the quality of particle according to flying speed.
(2), can draw the relational expression of the quality of particle flying speed and single particle according to the law of conservation of momentum, aerodynamics and fluid mechanics principle, formula is as follows:
d m d = k C 1 + C 2 v + C 3 ln ( 1 - C 4 v ) - - - ( 1 )
Wherein: dm dBe the quality of a certain particle diameter single particle, v is the flying speed of particle, C 1Be systematic error correction factor, C 2Be particle flying speed correction factor, C 3Be the speed of gas, C 4Be the correction factor of gas velocity,
Figure BDA00003078901700023
L is velocity survey point and jet opening distance, and Z is the particle mobility.Draw number that the quality of a certain particle diameter individual particle thing can this particle diameter particle of root goes out this particle diameter particle through accumulation calculating gross mass.
(3), according to the particle diameter of particle and number concentration information, calculate the gross mass of a certain particle diameter particle, computing formula is as follows:
m d = Σ i = 0 N d m d - - - ( 2 )
In the formula, N is that the particle particle diameter is the total number of particles of d, dm dBe that the particle particle diameter is the quality of the individual particle thing of d, m dBe that particle diameter is the quality of the corresponding all particulates of d.After drawing the gross mass of a certain particle diameter particle, go out the particle gross mass of all particle diameter correspondences according to the range computation of particle diameter, the additions of the corresponding particle gross mass of all particle diameters are drawn particle gross mass in the particle size range, at last the mass concentration that draws the particle of surveying according to the flow that adopts and time.
(4), by the scope of Atmospheric particulates particle diameter, according to the mass concentration that the flow of sampling and sampling time calculate Atmospheric particulates, computing formula is as follows:
PM = Σ d = 0 D m d L · t - - - ( 3 )
In the formula, D is the maximum particle diameter of the measured Atmospheric particulates that arrive, and L is sampling flow, and t is the sampling time, and PM is the mass concentration of Atmospheric particulates.
(5), adopt standard aerosol particle electronic generator to produce the standard particle thing.Standard aerosol particle electronic generator aperture is selected 20 μ m, utilizes DOP solution to produce the standard particle thing of 20 groups of different solutions concentration.
(6), utilize aerodynamics grain spectrometer to measure the flight time of the standard particle thing of 20 groups of different solutions concentration that obtain in the step (5), calculate flying speed according to formula (6) by the flight time.Calculate the quality of the standard particle thing of 20 groups of different solutions concentration, mass particle is calculated by following formula:
m p = π 6 · D d 3 · ρ - - - ( 4 )
In the formula, ρ is the mass particle density of DOP; D dIt is liquid-drop diameter.
D dCan be obtained by following formula:
D d = ( 6 QC πf ) 1 / 3 - - - ( 8 )
Q is liquid supply rate in the formula, i.e. flow rate of liquid, and f is vibration frequency, C is volumetric concentration.
(7), quality and the flying speed data of the standard particle thing that produces under 20 groups of different solutions concentration that obtain in the step (6) are carried out match, adopt 5 order polynomial matches:
y=A+B 1x 1+B 2x 2+B 3x 3+B 4x 4+B 5x 5 (5)
Wherein, y is the inverse of the quality of individual particle thing, and x is the flight time of particle, A, B 1, B 2, B 3, B 4, B 5Be 5 order polynomial fitting parameters, adopt least square method to carry out obtaining parameter A, B behind the linear fit 1, B 2, B 3, B 4, B 5, and the corresponding matched curve of drawing.Fractional part is launched by Taylor's formula in the formula (1), finally determine C in the formula (1) according to the curve that match is come out 1, C 2, C 3, C 4, the k parameter.Formula (1) to fractional part by the Taylor's formula expansion formula as follows:
1 d m p = C 1 + C 2 v + C 3 ln ( 1 - C 4 v ) k
= C 1 k + C 2 v k + C 3 k ( - C 4 v - C 4 2 v 2 -
C 4 3 v 3 - C 4 4 v 4 - C 4 5 v 5 . . . . . . )
= C 1 k + C 2 - C 3 C 4 k v - C 3 C 4 2 k v 2 - - - - ( 6 )
C 3 C 4 3 k v 3 - C 3 C 4 5 k v 5 . . . . . .
In the formula: dm dBe the quality of a certain particle diameter single particle, v is the flying speed of particle, C 1Be systematic error correction factor, C 2Be particle flying speed correction factor, C 3Be the speed of gas, C 4Be the correction factor of gas velocity,
Figure BDA00003078901700041
L is velocity survey point and jet opening distance, and Z is the particle mobility.
Compare with existing Atmospheric particulates mass concentration measuring technique, the invention has the advantages that:
(1) the present invention comes inverting Atmospheric particulates mass concentration in conjunction with light scattering and flight time principle, can avoid being subjected to particle refractive index and the error that cause different with geometric configuration, thereby improves the inversion accuracy of Atmospheric particulates mass concentration.
(2) parameter that adopts match of the present invention to obtain need not to measure the accurate demarcation that systematic parameter such as two hot spot distances namely can realize the particle particle diameter.
(3) the present invention realizes the fast inversion of Atmospheric particulates PM10, PM2.5, PM1.
(4) the particle quality retrieving concentration among the present invention is to obtain by the measurement flight time, and laser instrument light-intensity variation meeting causes that scattered light intensity changes, but can not exert an influence to the flight time measurement result, thereby reduces measurement result to the susceptibility of environmental change.
Description of drawings
Fig. 1 is the realization flow figure of the inventive method.
Embodiment
As shown in Figure 1, it is as follows to the present invention is based on the Atmospheric particulates mass concentration inversion algorithm concrete steps of particle flight time:
The first step, can measure particle in the flight time of two hot spots by the aerodynamic size spectrometer, calculate the flying speed of particle according to the distance L of two hot spots, formula is as follows:
v = L Δt - - - ( 6 )
Wherein: v is the flying speed of particle, and L is the distance of two hot spots, and Δ t is that particle is in the flight time of two hot spots.Can draw the flying speed of particle by the flight time, draw the quality of particle according to flying speed.
Second step, particle be by after accelerating spout, on air trajectory more arbitrarily, every kind of size particles thing has unique speed u pAccording to theorem of momentum, the differential momentum conservation equation of each particle can be represented with formula (7) in the particle:
d dt ( m p u p ) = < &Delta; m p u p > + m p g - - - ( 9 )
Wherein, subscript p represents particle;
Figure BDA00003078901700044
Give the mean force of particle for gas molecule collision; Subscript g represents to carry gas; Z is the particle mobility; m pG is the gravity of particle self.
Because with respect to the mean force that gas molecule collision is given particle, the gravity of particle itself is very little, namely acceleration of gravity is very little with respect to the acceleration that gas molecule collision brings, and in computation process, can ignore the influence of gravity.Formula (9) is reduced to:
d dt ( m p u p ) = u g - u p Z - - - ( 10 )
Because two facula positions are very near apart from spout, for the ease of calculating, think Z and u gBe constant.Finally draw the relational expression of the quality of particle flying speed and single particle, formula is as follows:
d m d = k C 1 + C 2 v + C 3 ln ( 1 - C 4 v ) - - - ( 1 )
In the formula: dm dBe the quality of a certain particle diameter single particle, v is the flying speed of particle, C 1Be systematic error correction factor, C 2Be particle flying speed correction factor, C 3Be the speed of gas, C 4Be the correction factor of gas velocity, L is velocity survey point and jet opening distance, and Z is the particle mobility.Draw number that the quality of a certain particle diameter individual particle thing can this particle diameter particle of root goes out this particle diameter particle through accumulation calculating gross mass.
The 3rd step, according to the particle diameter of particle and number concentration information, calculate the gross mass of a certain particle diameter particle, computing formula is as follows:
m d = &Sigma; i = 0 N d m d - - - ( 2 )
In the formula, N is that the particle particle diameter is the total number of particles of d, dm dBe that the particle particle diameter is the quality of the single particle of d, m dBe particle diameter by d the quality of all particles of correspondence.After drawing the gross mass of a certain particle diameter particle, go out the particle gross mass of all particle diameter correspondences according to the range computation of particle diameter, the additions of the corresponding particle gross mass of all particle diameters are drawn particle gross mass in the particle size range, at last the mass concentration that draws the particle of surveying according to the flow that adopts and time.
The 4th step, by the scope of Atmospheric particulates particle diameter, according to the mass concentration that the flow of sampling and sampling time calculate Atmospheric particulates, computing formula is as follows:
PM = &Sigma; d = 0 D m d L &CenterDot; t - - - ( 3 )
In the formula, D is the maximum particle diameter of Atmospheric particulates, and L is sampling flow, and t is the sampling time, and PM is the mass concentration of Atmospheric particulates.
The 5th step, employing standard aerosol particle electronic generator produce the standard particle thing.Aperture is selected 20 μ m, utilizes DOP solution to produce the standard particle thing of 20 groups of different solutions concentration.
The 6th step, utilize aerodynamics grain spectrometer to measure the flight time of the standard particle thing of 20 groups of different solutions concentration that the 5th step obtained in described, calculate flying speed according to formula (6) by the flight time.Calculate the quality of the standard particle thing of 20 groups of different solutions concentration, mass particle is calculated by following formula:
m p = &pi; 6 &CenterDot; D d 3 &CenterDot; &rho; - - - ( 4 )
In the formula, ρ is the mass particle density of DOP; D dIt is liquid-drop diameter.
D dCan be obtained by following formula:
D d = ( 6 QC &pi;f ) 1 / 3 - - - ( 8 )
Q is liquid supply rate in the formula, i.e. flow rate of liquid, and f is vibration frequency, C is volumetric concentration.
The 7th step, the 6th quality and the flying speed data that go on foot the standard particle thing that produces under 20 groups of different solutions concentration drawing are carried out match, adopt 5 order polynomial matches:
y=A+B 1x 1+B 2x 2+B 3x 3+B 4x 4+B 5x 5 (5)
Wherein, y is the inverse of the quality of individual particle thing, and x is the flight time of particle, A, B 1, B 2, B 3, B 4, B 5Be 5 order polynomial fitting parameters, adopt least square method to carry out obtaining parameter A, B behind the linear fit 1, B 2, B 3, B 4, B 5, and the corresponding matched curve of drawing, fractional part is launched by Taylor's formula in the formula (1), obtain formula (9), finally determine C in the formula (1) according to the parameter that match is come out 1, C 2, C 3, C 4, the k parameter.
1 d m p = C 1 + C 2 v + C 3 ln ( 1 - C 4 v ) k
= C 1 k + C 2 v k + C 3 k ( - C 4 v - C 4 2 v 2 -
C 4 3 v 3 - C 4 4 v 4 - C 4 5 v 5 . . . . . . )
= C 1 k + C 2 - C 3 C 4 k v - C 3 C 4 2 k v 2 - - - - ( 9 )
C 3 C 4 3 k v 3 - C 3 C 4 5 k v 5 . . . . . .
In the formula: dm dBe the quality of a certain particle diameter single particle, v is the flying speed of particle, C 1Be systematic error correction factor, C 2Be particle flying speed correction factor, C 3Be the speed of gas, C 4Be the correction factor of gas velocity,
Figure BDA00003078901700071
L is velocity survey point and jet opening distance, and Z is the particle mobility.
Y=A+B 1x 1+ B 2x 2+ B 3x 3+ B 4x 4+ B 5x 5The physical meaning of all symbols of formula;
The Atmospheric particulates flight time that the 8th step, basis record converts the flight time to flying speed, finally is finally inversed by the mass concentration of Atmospheric particulates through above-mentioned steps by computing machine.
The non-elaborated part of the present invention belongs to techniques well known.
The above; only for part embodiment of the present invention, but protection scope of the present invention is not limited thereto, and any those skilled in the art are in the technical scope that the present invention discloses; the variation that can expect easily or replacement all should be encompassed within protection scope of the present invention.

Claims (2)

1. Atmospheric particulates mass concentration inversion method based on the particle flight time is characterized in that performing step is as follows:
(1) data message that measures by the aerodynamic size spectrometer draws the relational expression of the quality of particle flying speed and single particle according to the law of conservation of momentum, aerodynamics and fluid mechanics principle, and formula is as follows:
d m d = k C 1 + C 2 v + C 3 ln ( 1 - C 4 v ) - - - ( 1 )
In the formula, C 1Be systematic error correction factor, C 2Be particle flying speed correction factor, C 3Be the speed of gas, C 4Be the correction factor of gas velocity,
Figure FDA00003078901600012
L is velocity survey point and jet opening distance, and Z is the particle mobility, and v is the flying speed of particle, dm dIt is the quality of a certain particle diameter individual particle thing; The number that draws this particle diameter particle of quality root of a certain particle diameter individual particle thing goes out the gross mass of this particle diameter particle through accumulation calculating;
(2) according to particle diameter and the number concentration information of particle, calculate the gross mass of a certain particle diameter particle, computing formula is as follows:
m d = &Sigma; i = 0 N d m d - - - ( 2 )
In the formula, N is that the particle particle diameter is the particle sum of d, dm dBe that the particle particle diameter is the quality of the corresponding individual particle thing of d, m dBe that particle diameter is the gross mass of the corresponding particle of d; After drawing the gross mass of a certain particle diameter particle, go out the particle gross mass of all particle diameter correspondences according to the range computation of particle diameter, the additions of the corresponding particle gross mass of all particle diameters are drawn particle gross mass in the particle size range, at last the mass concentration that draws the particle of surveying according to the flow that adopts and time;
(3) by measured Atmospheric particulates particle size range, according to flow and the sampling time mass concentration that calculates Atmospheric particulates of sampling, computing formula is as follows:
PM = &Sigma; d = 0 D m d L &CenterDot; t - - - ( 3 )
In the formula, D is maximum particle diameter in the measured Atmospheric particulates, and L is sampling flow, and t is the sampling time, and PM is the mass concentration of Atmospheric particulates.
2. according to claims 1 described a kind of Atmospheric particulates mass concentration inversion method based on the particle flight time, it is characterized in that: the system calibrating coefficient method of described step (1) is as follows:
(11) produce the standard particle thing with standard aerosol particle electronic generator, the aperture of standard aerosol particle electronic generator is selected 20 μ m, utilizes DOP solution to produce the standard particle thing of 20 groups of different solutions concentration;
(12) utilize the aerodynamic size spectrometer to measure the flight time of the standard particle thing of the described 20 groups of different solutions concentration that obtain of step (11), calculate flying speed by the flight time, calculate the quality of the standard particle thing of 20 groups of different solutions concentration that obtain described in the step (11), mass particle is calculated by following formula:
m p = &pi; 6 &CenterDot; D d 3 &CenterDot; &rho; - - - ( 4 )
In the formula, ρ is the mass particle density of DOP; D dIt is liquid-drop diameter;
(13) quality and the flying speed of the standard particle thing that produces under 20 groups of different solutions concentration that obtain described in the step (12) are carried out match, adopt 5 order polynomial matches:
y=A+B 1x 1+B 2x 2+B 3x 3+B 4x 4+B 5x 5 (5)
Wherein, y is the inverse of the quality of individual particle thing, and x is the flight time of particle, A, B 1, B 2, B 3, B 4, B 5Be 5 order polynomial fitting parameters, adopt least square method to carry out obtaining parameter A, B behind the linear fit 1, B 2, B 3, B 4, B 5, and provide corresponding matched curve, formula (1) fractional part is launched by Taylor's formula, finally determine C in the formula (1) according to the parameter that match is come out 1, C 2, C 3, C 4, the k parameter; Formula (1) to fractional part by the Taylor's formula expansion formula as follows:
1 d m p = C 1 + C 2 v + C 3 ln ( 1 - C 4 v ) k
= C 1 k + C 2 v k + C 3 k ( - C 4 v - C 4 2 v 2 -
C 4 3 v 3 - C 4 4 v 4 - C 4 5 v 5 . . . . . . )
= C 1 k + C 2 - C 3 C 4 k v - C 3 C 4 2 k v 2 - - - - ( 6 )
C 3 C 4 3 k v 3 - C 3 C 4 5 k v 5 . . . . . .
In the formula: dm dBe the quality of a certain particle diameter single particle, v is the flying speed of particle, C 1Be systematic error correction factor, C 2Be particle flying speed correction factor, C 3Be the speed of gas, C 4Be the correction factor of gas velocity,
Figure FDA00003078901600027
L is velocity survey point and jet opening distance, and Z is the particle mobility.
CN201310139285.2A 2013-04-21 2013-04-21 A kind of Atmospheric particulates mass concentration inversion method based on the particulate matter flight time Active CN103234882B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310139285.2A CN103234882B (en) 2013-04-21 2013-04-21 A kind of Atmospheric particulates mass concentration inversion method based on the particulate matter flight time

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310139285.2A CN103234882B (en) 2013-04-21 2013-04-21 A kind of Atmospheric particulates mass concentration inversion method based on the particulate matter flight time

Publications (2)

Publication Number Publication Date
CN103234882A true CN103234882A (en) 2013-08-07
CN103234882B CN103234882B (en) 2016-08-24

Family

ID=48882933

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310139285.2A Active CN103234882B (en) 2013-04-21 2013-04-21 A kind of Atmospheric particulates mass concentration inversion method based on the particulate matter flight time

Country Status (1)

Country Link
CN (1) CN103234882B (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104122179A (en) * 2014-08-05 2014-10-29 云南中烟工业有限责任公司 Method for evaluating smoke volume of electronic cigarettes
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
CN108120661A (en) * 2017-12-19 2018-06-05 北京理工大学 Particle content spatial and temporal distributions assay method in a kind of urban air
CN108709836A (en) * 2018-07-26 2018-10-26 宁夏大学 Aerosol detection method and system
CN109632589A (en) * 2018-12-30 2019-04-16 江苏苏净集团有限公司 A kind of Atmospheric particulates detection device and method
CN109738345A (en) * 2019-01-17 2019-05-10 中国科学院城市环境研究所 A kind of individual particle aerosol real-time quantitative analysis method
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)

* Cited by examiner, † Cited by third party
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

Patent Citations (2)

* Cited by examiner, † Cited by third party
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 (3)

* Cited by examiner, † Cited by third party
Title
MICHAEL H. SCHWARTZ: "《THEORETICAL BASIS OF THE TIME-OF-FLIGHT AEROSOL SPECTROMETER: A METHOD FOR MONITORING THE SIZE DISTRIBUTION OF SUBMICRON AEROSOL PARTICLES》", 《JOURNAL OF AEROSOL SCIENCE>, vol. 7, 31 December 1976 (1976-12-31), pages 281 - 296 *
李海军 等.: "《空气动力学粒径谱与微量振荡天平颗粒物质量浓度的测量比较》", 《大气与环境光学学报》, vol. 4, no. 4, 31 July 2009 (2009-07-31), pages 315 - 320 *
邢建永: "《空气动力学粒谱分析仪标定方法研究》", 《大气环境科学学报》, vol. 2, no. 3, 31 May 2007 (2007-05-31), pages 211 - 213 *

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104122179A (en) * 2014-08-05 2014-10-29 云南中烟工业有限责任公司 Method for evaluating smoke volume of electronic cigarettes
CN104122179B (en) * 2014-08-05 2017-03-22 云南中烟工业有限责任公司 Method for evaluating smoke volume of electronic cigarettes
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
CN108120661A (en) * 2017-12-19 2018-06-05 北京理工大学 Particle content spatial and temporal distributions assay method in a kind of urban air
CN108709836A (en) * 2018-07-26 2018-10-26 宁夏大学 Aerosol detection method and system
CN108709836B (en) * 2018-07-26 2024-03-19 宁夏大学 Aerosol detection method and system
CN109632589A (en) * 2018-12-30 2019-04-16 江苏苏净集团有限公司 A kind of Atmospheric particulates detection device and method
CN109632589B (en) * 2018-12-30 2024-03-12 江苏苏净集团有限公司 Atmospheric particulate detection device and method
CN109738345A (en) * 2019-01-17 2019-05-10 中国科学院城市环境研究所 A kind of individual particle aerosol real-time quantitative analysis 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

Also Published As

Publication number Publication date
CN103234882B (en) 2016-08-24

Similar Documents

Publication Publication Date Title
CN103234882A (en) Method for inverting mass concentration of atmospheric particulates based on flight time of particulates
Iungo et al. Field measurements of wind turbine wakes with lidars
ES2948941T3 (en) Emission detection and monitoring method and system
Zhang et al. Measurements of dust deposition velocity in a wind-tunnel experiment
ITFI20100208A1 (en) METHOD FOR QUANTIFYING A FLOW OF GAS FUGITIVE BY MEANS OF VERTICAL CONCENTRATION MEASUREMENTS
Feng et al. Computational simulations of blown sand fluxes over the surfaces of complex microtopography
CN108205164A (en) A kind of atmospheric visibility parametrization Forecasting Methodology based on WRF-Chem
Girdwood et al. Design and field campaign validation of a multi-rotor unmanned aerial vehicle and optical particle counter
Cauteruccio et al. Wind tunnel validation of a particle tracking model to evaluate the wind‐induced bias of precipitation measurements
CN104819963A (en) Measurement method and monitoring system of atmosphere vertical visibility
CN103472035A (en) Instrument for measuring moisture absorption characteristic and body angle scattering coefficient of atmospheric aerosol
CN110006849B (en) Method and device for obtaining extinction coefficient of aerosol
Kukačka et al. Wind tunnel measurement of turbulent and advective scalar fluxes: a case study on intersection ventilation
JP5131400B1 (en) Search method of unsteady dust source position of falling dust
CN109507072A (en) A kind of fine particle turbulent flux measurement method
KR20170116805A (en) Method for retrieving aerosol height using Raman scattering property of atmospheric molecules based on sunlight measurement in multi-angle
He et al. Identification of stratospheric disturbance information in China based on round-trip intelligent sounding system
Yassin et al. Experimental study on flow and gaseous diffusion behind an isolated building
Meyer-Kornblum et al. Gap-filling fast electrical mobility spectrometer measurements of particle number size distributions for eddy covariance application
JP5505463B2 (en) Search method for unsteady dust generation source of falling dust
Gu et al. Research on the fractal model and calibration of the aerosol mass concentration measurement based on the particle group light scattering
Zhang et al. Detection of Particle Concentration and Particle Size Based on Aerodynamic Particle Size Spectrometer
Zhang et al. A novel optical instrument for measuring mass concentration and particle size in real time
Strunin et al. Response properties of atmospheric turbulence measurement instruments using Russian research aircraft
JP5073861B1 (en) Search method of unsteady dust source position of falling dust

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant