Particulate matter measurement apparatus and method
10502710 ยท 2019-12-10
Assignee
Inventors
- Simone HOCHGREB (Cambridge, GB)
- Robert NISHIDA (Cambridge, GB)
- Adam Boies (Cambridge, GB)
- John SAFFELL (Cambridge, GB)
Cpc classification
B03C3/47
PERFORMING OPERATIONS; TRANSPORTING
B03C3/017
PERFORMING OPERATIONS; TRANSPORTING
B03C3/025
PERFORMING OPERATIONS; TRANSPORTING
International classification
G01N27/62
PHYSICS
B03C3/017
PERFORMING OPERATIONS; TRANSPORTING
B03C3/38
PERFORMING OPERATIONS; TRANSPORTING
B03C3/47
PERFORMING OPERATIONS; TRANSPORTING
B03C3/02
PERFORMING OPERATIONS; TRANSPORTING
Abstract
Particle measurement apparatus comprises an inlet for receiving a gas sample for analysis, a photoionisation chamber, at least one light source arranged to illuminate an interior of the photoionisation chamber, first and second electrodes coupled to a power source and configured to provide a DC potential difference across at least a portion of the photoionisation chamber, and an outlet, together defining a gas flow path from the inlet, through the photoionisation chamber, and towards the outlet.
Claims
1. Particulate matter measurement apparatus comprising an inlet for receiving a gas sample for analysis, a photoionisation chamber, at least one light source arranged to illuminate an interior of the photoionisation chamber to photoionize particulate matter in the gas sample, first and second electrodes coupled to a power source and configured to provide a DC potential difference across at least a portion of the photoionisation chamber, and an outlet, together defining a gas flow path from the inlet, through the photoionisation chamber, and towards the outlet.
2. The apparatus of claim 1 further comprising at least one electrode current sensor configured to measure an electrode current flowing to or from at least one of the first and second electrodes.
3. The apparatus according to claim 2 further comprising a charged particulate matter detector and at least one detector current sensor configured to measure a detector current flowing from the charged particulate matter detector.
4. The apparatus according to claim 3 further comprising a comparator circuit configured to compare the electrode current, measured by the at least one electrode current sensor, and the detector current, measured by the at least one detector current sensor.
5. The apparatus according to claim 3 further comprising a processor configured to process the electrode current, measured by the at least one electrode current sensor, and the detector current, measured by the at least one detector current sensor, to determine a particulate matter concentration and/or size parameter of the particulate matter.
6. The apparatus of claim 3, further comprise a comparator circuit is configured to compare the electrode current, measured by the at least one electrode current sensor, and the detector current, measured by the at least one detector current sensor to determine a particulate matter concentration and/or size parameter of the particulate matter.
7. The apparatus according to claim 1, wherein the potential difference provided by the first and second electrodes is variable between at least first and second different DC voltages.
8. The apparatus according to claim 7, wherein the potential difference provided by the first and second electrodes is maintainable at each of the at least first and second different DC voltages for at least 0.5 seconds.
9. The apparatus according to claim 7, wherein the potential difference provided by the first and second electrodes is variable between the at least first and second different DC voltages at a frequency of less than 2 Hz.
10. The particulate measurement apparatus of claim 1 further comprising: a plurality of additional electrodes coupled to an additional power supply and configured to provide at least an additional potential difference across another portion of the photoionisation chamber concurrently with the potential difference provided across the portion of the photoionisation chamber.
11. The apparatus of claim 1, wherein the light source is an ultraviolet light source configured to emit ultraviolet light.
12. The apparatus of claim 1, wherein the light source is an ultraviolet light source configured to emit ultraviolet light within a range of 150 nm to 260 nm.
13. A method of using a particulate matter measurement apparatus, the method comprising: receiving a gas sample for analysis using an inlet, providing a photoionisation chamber, illuminating an interior of the photoionisation chamber using at least one light source to photoionize particulate matter in the gas sample; coupling first and second electrodes to a power source to provide a DC potential difference across at least a portion of the photoionisation chamber, and providing an outlet, together defining a gas flow path from the inlet, through the photoionisation chamber, and towards the outlet.
14. The apparatus of claim 1, wherein the particulate matter is soot particles.
15. Particulate matter measurement apparatus comprising an inlet for receiving a gas sample for analysis, a photoionisation chamber, first and second electrodes, at least one light source arranged to illuminate an interior of the photoionisation chamber between the first and second electrodes to photoionize particulate matter in the gas sample, at least one electrode current sensor configured to measure an electrode current flowing to or from at least one of the first and second electrodes, and an outlet, together defining a gas flow path from the inlet, through the photoionisation chamber between the first and second electrodes, and towards the outlet.
16. The method according to claim 13 wherein the light source is an ultraviolet light source configured to emit ultraviolet light within a range of 150 nm to 260 nm.
17. The method of claim 16 applying another potential difference concurrently with the potential difference provided across the portion of the photoionisation chamber, by way of a plurality of additional electrodes, across another portion of the photoionisation chamber through which sample gas flows; and measuring one or more electrode currents flowing to or from at least one electrode from the plurality of additional electrodes.
18. The method of claim 16 further comprising measuring an electrode current flowing to or from at least one of the first and second electrodes using at least one electrode current sensor.
19. The method according to claim 18 further comprising providing a charged particulate matter detector and measuring a detector current flowing from the charged particulate matter detector using at least one detector current sensor.
20. The method according to claim 19 further comprising comparing, using a comparator circuit, the electrode current measured by the at least one electrode current sensor and the detector current measured by the at least one detector current sensor.
21. The method according to claim 20 further comprising using the electrode current measured by the at least one electrode current sensor and the detector current measured by the at least one detector current sensor to determine a particulate matter concentration and/or size parameter of the particulate matter.
22. The method according to claim 19 further comprising processing, using a processor, the electrode current, measured by the at least one electrode current sensor, and the detector current, measured by the at least one detector current sensor, to determine a particulate matter concentration and/or size parameter of the particulate matter.
23. The method according to claim 16, wherein the potential difference provided by the first and second electrodes is variable between at least first and second different DC voltages.
24. The method according to claim 23, wherein the potential difference provided by the first and second electrodes is maintainable at each of the at least first and second different DC voltages for at least 0.5 seconds.
25. The method according to claim 23, wherein the potential difference provided by the first and second electrodes is variable between the at least first and second different DC voltages at a frequency of less than 2 Hz.
26. The method according to claim 16 wherein the light source is an ultraviolet light source configured to emit ultraviolet light.
27. The method according to claim 16 wherein the particulate matter is soot particles.
Description
DESCRIPTION OF THE DRAWINGS
(1) An example embodiment of the present invention will now be illustrated with reference to the following Figures in which:
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DETAILED DESCRIPTION OF EXAMPLE EMBODIMENTS
(21) First Example Embodiment of the Invention
(22) In a first example embodiment, as illustrated in
(23) The interior of the sensor body 2 is hollow. The interior of the sensor body 2 forms an elongate photoionisation chamber 12 (see
(24) A photoionisation lamp 17 is provided at the first end of the sensor body. The photoionisation lamp 17 is coupled to a power supply (not shown). The photoionisation lamp is configured to emit, in use, ultraviolet light having wavelengths within the range 150 nm-260 nm. The photoionisation lamp is oriented such that emitted ultraviolet light illuminates the entirety of the photoionisation chamber 12.
(25) A Faraday cup electrometer 18 as is generally known in the field of particle detectors is mounted in the collector chamber 10. The Faraday cup electrometer 18 typically consists of an electrically conductive filter (not shown) mounted within a wire mesh (not shown). The Faraday cup electrometer 18 is positioned within the collector chamber 10 such that flow of gas from the photoionisation chamber 12 and into the collector chamber 10 passes through the Faraday cup electrometer 18. In use, any charged particles exiting the photoionisation chamber 12 through the outlet 7 are incident on the Faraday cup electrometer 18. An electrical outlet of the Faraday cup electrometer is connected to earth 19 in series with an ammeter 20.
(26) In use, a gas sample for analysis is pumped into the sensor through the inlet by the pump. Sample gas consequently flows sequentially through the inlet passageway, into and through the photoionisation chamber from the first end towards the second end, and through the outlet passageway to the outlet. The pump is configured to pump the gas sample through the sensor at a known, generally constant gas flow rate.
(27) The power supply connected to the photoionisation lamp 17 is switched on such that the lamp illuminates the photoionisation chamber 12 with ultraviolet light. The gas sample generally comprises a mixture of gaseous atoms and/or molecules and particles suspended in the gas. The gas molecules and/or atoms, as well as the particles, are typically uncharged (i.e. electrically neutral). As the gas sample flows through the photoionisation chamber, particles in the gas sample absorb one or more photons of ultraviolet light emitted by the photoionisation lamp. The wavelength of the ultraviolet light is selected such that absorption of a photon by a particle causes that particle to emit a photoelectron. The wavelength of ultraviolet light emitted by the photoionisation lamp is therefore below a threshold wavelength for particle photoionisation (that is to say, each photon emitted by the photoionisation lamp has an energy above a threshold energy required for particle photoionisation). Absorption of a photon and consequent emission of an electron causes a particle to acquire a net positive charge. Each electron which is emitted by a particle on photoionisation generally proceeds to ionise a nearby gas atom or molecule, thereby forming a negatively charged gas ion. Photoionisation of the particles in the gas sample takes place between the first and second electrodes 13,14.
(28) When the power supply 15 connected to the electrodes 13,14 is switched off, after a characteristic period of time (dependent on, inter alia, the concentration of particles in the gas), negatively charged gas ions and positively charged particles in the gas sample in the photoionisation chamber 12 are attracted to one another and tend to come into contact with one another, resulting in the transfer of electrons back from the ions to the particles, thereby neutralising both charges in a process called recombination. Consequently, only a portion of the particles in the gas sample exiting the photoionisation chamber 12 at the second end 9 and flowing over the Faraday cup electrometer 18 in the collector chamber 10 are electrically charged. While a collector signal measured by the ammeter 20 is detectable, the strength of the signal is typically only partially correlated to the number and size of the particles in the gas sample. Therefore, the sensitivity of the particle detector 1, when the power supply 15 is switched off, is relatively poor.
(29) However, when the power supply 15 connected to the electrodes 13,14 is switched on, a substantially uniform DC potential difference V is provided across the photoionisation chamber between the first and second electrodes 13,14. The applied potential difference V typically generates an electric field of between around 1 V/cm to around 100 V/cm across the photoionisation chamber. This mode is illustrated schematically in
(30) In contrast, because the positively charged particles 22 are significantly less mobile than the gas ions, the charged particles 22 tend to flow through the photoionisation chamber 12 and through the outlet without being captured by the ion trap. If the photoionisation of particles in the gas sample within the photoionisation chamber 12 is sufficiently high for detectability, the flux of charged particles onto the Faraday cup electrometer 18, and thus the collector signal measured by the ammeter 20, is proportional to a combined parameter N.sup.D.sup., in some instances proportional to a measurement of the total effective particle surface area in the gas sample, where N is the concentration of particles in the gas and D is the average particle diameter. The sensor may therefore be calibrated in order to provide a measurement of this total effective particle surface area. The total effective particle surface area measured by the sensor in this mode is more accurate than that detected when no potential difference is applied between the first and second electrodes 13,14.
(31) In this first example embodiment, the measured anode current and the measured collector current are both typically dependent on the total effective particle surface area. The gas sensor may therefore be calibrated to output a total effective particle surface area based on measurement of either the electrode current or the collector current.
(32) Second Example Embodiment of the Invention
(33) In a second embodiment of the invention, the output of the DC power supply 15 in
(34) When the first voltage V.sub.1 is applied between the first and second electrodes 13,14, the sensor operates in essentially the same mode as outlined above for the first embodiment of the invention and as illustrated in
(35) When the potential difference between the first and second electrodes 13,14 is increased to voltage V.sub.2, however, the force exerted on the negatively charged gas ions 21, the free electrons and the positively charged particles 22 in the gas sample flowing through the photoionisation chamber 12 is increased. This typically results in a greater proportion of the negatively charged gas ions 21 and free electrons being trapped by the second electrode 14, resulting in both an increased electrode current. Additionally, as illustrated schematically in
(36) For a given applied voltage between the first and second electrodes 13,14 and a given flow rate of sample gas through the photoionisation chamber 12, the dependence of the electrode current on the particle concentration N and the mean particle diameter D can be modelled according to
I.sub.e=a.sub.eN.sup..sup.
(37) The inventors have found that dimensionless parameters .sub.e and .sub.e are functions of the magnitude of the applied potential difference and typically take values between 0.5 and 3.
(38) Similarly, the dependence of the collector current on the particle concentration N and the mean particle diameter D can be modelled according to
I.sub.c=a.sub.cN.sup..sup.
(39) Again, the inventors have found that dimensionless parameters .sub.c and .sub.c are functions of the magnitude of the applied potential difference and typically take values between 0.5 and 3.
(40) Accordingly, by measuring both the electrode current and the collector current at a first applied voltage V.sub.1 and at a second applied voltage V.sub.2, equations (1) and (2) may be solved simultaneously to determine both N and D. Consequently, both the particle concentration and the mean particle diameter may both be determined independent of one another from one set of measurements, providing more detailed information about the particles in the gas sample than can be determined using only the first embodiment of the invention.
(41) In a variation of the second example embodiment of the invention, the potential difference applied between the first and second electrodes is varied between a plurality of different voltages (for example, the potential difference may be varied between 10 different voltages). For each additional voltage, the electrode and the collector currents change, thereby providing two more equations (1) and (2) which may be solved to determine N and D. The inventors have therefore found that by increasing the number of different voltages applied sequentially across the photoionisation chamber, the accuracy to which the particle concentration and mean particle diameter may be determined is increased.
(42) Third Example Embodiment of the Invention
(43) In a third embodiment of the invention, as illustrated in
(44) In use, a gas sample is pumped by the pump through the inlet 6, into and through the photoionisation chamber 12, and out through the outlet 7. Particles in the gas sample are photoionised by ultraviolet light emitted by the photoionisation lamp 17, thereby forming positively charged particles and negatively charged gas ions. As the particles and ions flow through the photoionisation chamber 12, they are deflected away from a general flow direction by the applied potential differences. As the gas flows between the first cathode-anode pair, all of the gas ions are trapped by the first anode 27. In this region, the potential difference V.sub.3 is however not strong enough to trap any of the positively charged particles. As the positively charged particles subsequently flow through the stronger potential difference V.sub.4 provided between the second cathode-anode pair, some of the smaller charged particles are trapped by the second cathode 25. Additionally, as the remaining positively charged particles subsequently flow through the even stronger potential difference V.sub.5 provided between the third cathode-cathode pair, even more of the smaller particles and some of the larger particles are trapped by the third cathode 26. Any remaining positively charged particles in the gas flow not trapped by any of the three electrode pairs flow out of the photoionisation chamber 12 and are detected by the Faraday cup electrometer 18.
(45) Accordingly, four currents are measured: three electrode currents corresponding to the current flowing between each of the three anode-cathode pairs and one detector current. Each of these four currents may be related to the particle concentration and mean particle diameter in the gas sample according to the following equations:
I.sub.e1=a.sub.e1N.sup..sup.
I.sub.e1=a.sub.e2N.sup..sup.
I.sub.e3=a.sub.e3N.sup..sup.
and
I.sub.c=a.sub.cN.sup..sup.
where the subscripts e1, e2 and e3 indicate each of the first, second and third electrode pairs respectively. By measuring the three electrode currents and one detector current, the concentration and mean diameter of particles trapped by each electrode pair or escaping from the photoionisation chamber to the detector can be determined simultaneously. A particle size distribution of particles in the gas sample may therefore be determined.
Fourth Example Embodiment of the Invention
(46) In a fourth example embodiment of the invention, as illustrated in
(47) Fifth Example Embodiment of the Invention
(48) In a fifth example embodiment of the invention, as illustrated in
(49) Further variations and modifications may be made within the scope of the invention herein disclosed.
(50) The pump need not be coupled to the inlet passageway as is shown in
(51) Sixth Example Embodiment of the Invention
(52) In a sixth example embodiment of the invention, when the output of the DC power supply 15 in
(53) Seventh Example Embodiment of the Invention
(54) In a seventh example embodiment of the invention, when the output of the DC power supply 15 in
(55) When the output of the DC power supply 54 in
(56) Experimental results
(57) Experimental results achieved using a sensor of the type illustrated schematically in
(58) The particle size and concentration were measured by aerosol characterization instrumentation. The number-weighted particle mobility diameter distribution was measured in parallel with the photoionization chamber for aerosol characterization using a Scanning Mobility Particle Sizer (SMPS; TSI Inc.: 3080 Electrostatic Classier, 3081 Differential Mobility Analyzer [DMA], 3025 Condensation Particle Counter [CPC]). The number-weighted mobility diameter distribution gives a measure of mean particle size and total concentration of aerosol particles.
(59) A sample flow of carbonaceous soot particles was produced by flows of propane (65-105 std. cm.sup.3/min), air (1.2 std. L/min), and N.sub.2 (3 std. L/min) in a co-flow inverse diffusion flame. An ejector diluter with filtered compressed air was used to provide a vacuum to draw the sample gas into the photoionisation chamber. The concentration of particles in the gas flow was varied by changing a diameter of a critical orifice (for example, 0.635 mm) and the flow rate of dilution air. The particle size was varied by changing the flow rate of propane into the flame (higher flow rates yielding larger particle sizes). Stainless steel and conductive silicon tubing were used to minimize particle losses in the sampling lines. Semivolatile organic carbon was removed from the sample gas using a catalytic stripper operated with an internal gas temperature of 350 C. An electrostatic precipitator operated at 3 kV was used to capture particles having any residual charge from the combustion process before they entered the photoionisation chamber and aerosol characterization equipment. The orifice diameter, the flow rate and the voltage state were held constant after any change in each said parameter until a steady state reading could be measured by both the photoionization instrumentation (Keithley and TSI Aerosol Electrometers) and the aerosol characterization instrumentation, taking up to 5 minutes per measurement.
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I.sub.c=a.sub.cN.sup..sup.
(63) Accordingly,
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(that is to say, the exponent is normalised such that the power of N in Equation (7) is 1) as a function of the applied potential difference using both the Keithley electrometer and the aerosol electrometer. The normalised exponent, a, is particularly sensitive to changes in the ion trap voltage. This means that the sensor may be calibrated such that, when the current is measured at two different trap voltages, both the particle concentration and the particle diameter may be independently determined.
(66)
(67) Nevertheless, despite the large effect of housing wall photoemission which causes a significant non-zero electrode current to flow even at zero particle concentration, the electrode current does remain a function of particle concentration for all applied voltages tested (in a range of between 8.5 V and 88 V). It is therefore also possible to calibrate the sensor to output a measured particle concentration and diameter without explicitly determining the housing wall photoemission contribution to the electrode current or explicitly compensating the electrode current for this background contribution. For example,