US20010042843A1 - Air content determination - Google Patents
Air content determination Download PDFInfo
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- US20010042843A1 US20010042843A1 US09/774,157 US77415701A US2001042843A1 US 20010042843 A1 US20010042843 A1 US 20010042843A1 US 77415701 A US77415701 A US 77415701A US 2001042843 A1 US2001042843 A1 US 2001042843A1
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- gas
- ozone
- concentration
- equilibrium
- nitrogen dioxide
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- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N33/00—Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
- G01N33/0004—Gaseous mixtures, e.g. polluted air
- G01N33/0009—General constructional details of gas analysers, e.g. portable test equipment
- G01N33/0027—General constructional details of gas analysers, e.g. portable test equipment concerning the detector
- G01N33/0036—Specially adapted to detect a particular component
- G01N33/0039—Specially adapted to detect a particular component for O3
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- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N27/00—Investigating or analysing materials by the use of electric, electrochemical, or magnetic means
- G01N27/02—Investigating or analysing materials by the use of electric, electrochemical, or magnetic means by investigating impedance
- G01N27/04—Investigating or analysing materials by the use of electric, electrochemical, or magnetic means by investigating impedance by investigating resistance
- G01N27/12—Investigating or analysing materials by the use of electric, electrochemical, or magnetic means by investigating impedance by investigating resistance of a solid body in dependence upon absorption of a fluid; of a solid body in dependence upon reaction with a fluid, for detecting components in the fluid
- G01N27/122—Circuits particularly adapted therefor, e.g. linearising circuits
- G01N27/123—Circuits particularly adapted therefor, e.g. linearising circuits for controlling the temperature
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- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N33/00—Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
- G01N33/0004—Gaseous mixtures, e.g. polluted air
- G01N33/0009—General constructional details of gas analysers, e.g. portable test equipment
- G01N33/0027—General constructional details of gas analysers, e.g. portable test equipment concerning the detector
- G01N33/0036—Specially adapted to detect a particular component
- G01N33/0037—Specially adapted to detect a particular component for NOx
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10—TECHNICAL SUBJECTS COVERED BY FORMER USPC
- Y10T—TECHNICAL SUBJECTS COVERED BY FORMER US CLASSIFICATION
- Y10T436/00—Chemistry: analytical and immunological testing
- Y10T436/11—Automated chemical analysis
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10—TECHNICAL SUBJECTS COVERED BY FORMER USPC
- Y10T—TECHNICAL SUBJECTS COVERED BY FORMER US CLASSIFICATION
- Y10T436/00—Chemistry: analytical and immunological testing
- Y10T436/11—Automated chemical analysis
- Y10T436/117497—Automated chemical analysis with a continuously flowing sample or carrier stream
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10—TECHNICAL SUBJECTS COVERED BY FORMER USPC
- Y10T—TECHNICAL SUBJECTS COVERED BY FORMER US CLASSIFICATION
- Y10T436/00—Chemistry: analytical and immunological testing
- Y10T436/17—Nitrogen containing
- Y10T436/177692—Oxides of nitrogen
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10—TECHNICAL SUBJECTS COVERED BY FORMER USPC
- Y10T—TECHNICAL SUBJECTS COVERED BY FORMER US CLASSIFICATION
- Y10T436/00—Chemistry: analytical and immunological testing
- Y10T436/17—Nitrogen containing
- Y10T436/177692—Oxides of nitrogen
- Y10T436/178459—Only nitrogen dioxide
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10—TECHNICAL SUBJECTS COVERED BY FORMER USPC
- Y10T—TECHNICAL SUBJECTS COVERED BY FORMER US CLASSIFICATION
- Y10T436/00—Chemistry: analytical and immunological testing
- Y10T436/17—Nitrogen containing
- Y10T436/177692—Oxides of nitrogen
- Y10T436/179228—Both nitrogen oxide and dioxide
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10—TECHNICAL SUBJECTS COVERED BY FORMER USPC
- Y10T—TECHNICAL SUBJECTS COVERED BY FORMER US CLASSIFICATION
- Y10T436/00—Chemistry: analytical and immunological testing
- Y10T436/20—Oxygen containing
- Y10T436/206664—Ozone or peroxide
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10—TECHNICAL SUBJECTS COVERED BY FORMER USPC
- Y10T—TECHNICAL SUBJECTS COVERED BY FORMER US CLASSIFICATION
- Y10T436/00—Chemistry: analytical and immunological testing
- Y10T436/25—Chemistry: analytical and immunological testing including sample preparation
- Y10T436/25875—Gaseous sample or with change of physical state
Definitions
- This invention relates generally to devices and methods for the detection of atmospheric components and, in particular, to devices and methods for the detection of nitrogen dioxide, nitrogen monoxide and ozone.
- Ozone, nitrogen dioxide and nitrogen monoxide are gases of particular relevance and it is desirable to monitor concentrations of these gases in air.
- Particular applications include roadside monitoring and atmosphere content monitoring.
- Ultraviolet light pushes the equilibrium to the right, forming nitrogen monoxide and ozone. This process involves irradiating a gas sample with ultraviolet light and then determining the final ozone concentration.
- This system further proposed that, once nitrogen dioxide had been determined, the concentration of nitrogen monoxide could subsequently be calculated after a separate reading of ozone produced by ultraviolet irradiation of a separate gas sample, scrubbed as before, with the addition of a further scrubber to remove ozone.
- a first aim of the present invention is to provide a cheaper, simpler and more reliable gas monitoring device, capable of accurate determination of nitrogen dioxide, nitrogen monoxide and/or ozone in air.
- One use for a cheaper, simple and more reliable gas monitoring device would be for measuring atmospheric composition at high altitudes. Typically, this is carried out by attaching sensors to a helium filled weather balloon and to launch the balloon into the atmosphere. The sensor then transmits data, usually via a radio link, as the balloon passes up through the atmosphere.
- the fact that the sensor is attached to a balloon places severe restrictions in terms of weight and cost on the sensor design.
- the cost aspect can be particularly critical, because generally such sensors have to be treated as disposable, given that they may be difficult to locate once they fall back to the ground. All of this can make it extremely difficult to produce a sensor which provides appropriately accurate readings that are continuous throughout the ascent of the balloon and which is capable of resisting the effects of high altitude and low temperature, where contaminants such as rain ice can affect sensor output.
- a second aim of the present invention is to provide a device that is suitably reliable, cheap and light to benefit high altitude gas monitoring.
- an instrument for assaying the concentration of one or more of nitrogen dioxide, nitrogen monoxide and/or ozone in an air sample comprising an equilibrium altering means for changing, or an element adapted to change, the equilibrium between nitrogen monoxide and nitrogen dioxide in the presence of ozone and oxygen, and a first gas sensor for quantifying the concentration of a first gas, being one of nitrogen dioxide, nitrogen monoxide or ozone; the instrument being adapted to measure the concentration of the first gas whilst the equilibrium between nitrogen monoxide and nitrogen dioxide in the presence of ozone and oxygen is altered and thereby to calculate the concentration of nitrogen dioxide, nitrogen monoxide and/or ozone in the air sample.
- the equilibrium altering means comprises an ultraviolet light source. More preferably, the ultraviolet light source is switched on and off periodically.
- the equilibrium altering means may comprise a means for adding, or an element adapted to add, one or more of nitrogen monoxide, nitrogen dioxide or ozone, and/or a means for removing, or an element adapted to remove, one or more of nitrogen monoxide, nitrogen dioxide, ozone or oxygen.
- the instrument is adapted to measure the concentration of the first gas at a plurality of time points and thereby monitor the rate at which the balance between nitrogen dioxide and nitrogen monoxide changes in response to the effects of the equilibrium altering means.
- the first gas sensor is an ozone sensor.
- the instrument may be adapted to allow for the effects of temperature and/or pressure on the equilibrium between nitrogen dioxide and nitrogen monoxide.
- a method of calculating the concentration of nitrogen dioxide, nitrogen monoxide and/or ozone in air comprising the steps of:
- the equilibrium altering means is an ultraviolet light source.
- the method includes the step of switching the ultraviolet source on and off periodically.
- the equilibrium altering means may comprise a means for adding, or an element adapted to add, one or more of nitrogen monoxide, nitrogen dioxide or ozone.
- the equilibrium altering means may comprise a means for removing, or an element adapted to remove, one or more of nitrogen monoxide, nitrogen dioxide, ozone or oxygen.
- the concentration of the first gas at a plurality of time points may be used to calculate the rate at which the balance between nitrogen dioxide and nitrogen monoxide changes in response to the effects of the equilibrium altering means.
- the readings may be of ozone concentration.
- the method may further include the step of allowing for the effects of temperature and/or pressure on the equilibrium between nitrogen dioxide and nitrogen monoxide.
- a computer program comprising program instructions which, when loaded onto a computer, are adapted to calculate, or constitute a processing means for calculating, the concentration of nitrogen monoxide, nitrogen dioxide and/or ozone in an air sample by the method of the second embodiment.
- a fourth aspect of the present invention there is provided a computer program according to the third aspect embodied on a record medium.
- sensing apparatus for detecting components in atmospheric air as the sensor is drawn up through the atmosphere, the sensor comprising:
- [0037] means for diverting, or an element adapted to divert, air through the shielding means and over the sensor element as the sensor passes through the atmosphere.
- the means for diverting air comprises a gas conducting member shaped to provide a pressure differential across the shielding means and cause air to move through the shielding means.
- the gas conducting member may be shaped to provide a low pressure region at an entry to the shielding means and thereby draw air through the shielding means into the gas conducting member.
- the gas conducting member may comprise a flow restricting member for diverting air that flows through the gas conducting member in use into the shielding means.
- the sensing apparatus may have an aperture to allow water or ice to flow out of the gas conducting member.
- sensing apparatus comprising:
- [0044] means for regulating, or an element adapted to regulate, the temperature of the sensor element by providing heat energy to the sensor element;
- [0045] means for calculating the air flow across the sensor element from the amount of heat energy supplied to the sensor element.
- the sensor apparatus may further comprise a means for measuring, or an element adapted to measure, the temperature of the sensor.
- FIG. 1 is a schematic diagram of an analytical system according to the present invention.
- FIG. 2 shows the response with time of ozone concentration in response to periodic ultraviolet irradiation, J;
- FIG. 3 shows the simulated variation of ozone, nitrogen monoxide and nitrogen dioxide concentrations in response to specific changes to the level of ultraviolet irradiation
- FIG. 4 shows the simulated variation of ozone, nitrogen monoxide and nitrogen dioxide concentrations in response to specific periodic changes to the level of ultraviolet irradiation
- FIG. 5 is a schematic cross-section through an example sensing apparatus
- FIG. 6 is an expanded view of a section of FIG. 5;
- FIG. 7 is a schematic cross-section through an alternative sensing apparatus.
- FIG. 8 is a schematic cross-section through a further sensing apparatus.
- FIG. 1 shows an example analytical system according to the present invention.
- the analytical system shown generally as 1 comprises an air inlet 2 which allows an air sample to enter irradiation chamber 3 .
- the irradiation chamber 3 comprises an ultraviolet source 4 and may be encased by an ultraviolet reflective surface 13 such as a metal foil.
- Air passes from the chamber outlet 5 to an external outlet 7 via an ozone sensor 10 .
- a pump (not shown) or airflow control means as discussed below may be provided to draw air through the external outlet 7 and through the sensor as a whole.
- ultraviolet light from the ultraviolet source 4 irradiates the air sample, driving the below reaction towards the formation of ozone and nitrogen monoxide:
- a processing means 20 such as a computer, microprocessor or other device having storage and processing capacity is provided to analyse the measurements and compute gas concentrations in the input gas sample.
- the invention further extends to the software used by said processing means 20 to control the switching on and off of the ultraviolet light source, record gas concentration readings from the sensor 10 and carry out gas concentration calculations.
- Said software may be provided on a digital storage means such as a magnetic or optical disk or solid state storage device such as EEPROM.
- the basis of the present invention is that readings of ozone concentration are taken not simply after the ratio of nitrogen monoxide to nitrogen dioxide has been modified by the influence of ultraviolet light or other factors and a steady state has been reached, but also either (a) during the process of this ratio being altered or (b) after or during the application of two different means for altering the ratio. The resulting readings are then used to calculate the concentrations of nitrogen monoxide, nitrogen dioxide and ozone in the gas sample.
- [O 3 ] is the instantaneous concentration of ozone
- [NO 2 ] is the instantaneous concentration of nitrogen dioxide
- [NO] is the instantaneous concentration of nitrogen monoxide
- J 1 is rate coefficient for photolysis of NO 2 , in units of per second
- k 2 is the rate constant for the reverse reaction.
- light is pulsed as shown in FIG. 2 which illustrates the periodic alteration of J with time and the resulting ozone concentration.
- FIG. 2 illustrates the periodic alteration of J with time and the resulting ozone concentration.
- the precise pulse shape of ozone concentration will depend on the gas flow rate, length of the ultraviolet irradiation zone, spectrum and intensity of ultraviolet source, gap between the end of irradiation zone and sensor and other calculable parameters.
- d[O 3 ]/dt under instrument irradiation can be used to give the concentration of nitrogen dioxide in the air sample.
- the characteristic relaxation time of a photolysed air sample gives the sum of the concentrations of nitrogen monoxide and nitrogen dioxide.
- the time resolved measurement of ozone therefore allows rates and relaxation time to be determined and so the concentrations of nitrogen monoxide, nitrogen dioxide and ozone can be determined.
- Temperature has an effect on the value of J 1 .
- the corresponding chemical step has a small activation energy thus temperature effects are small. If temperature effects need to be corrected this can be done using a simple measurement of temperature from a temperature measuring means (not shown). Pressure will have a still smaller effect and will preferably not be taken into account; however, it could be readily corrected for if required using readings from a pressure gauge (not shown). Pressure has a linear effect on the measured concentration for some types of ozone sensor as the partial pressure of ozone changes linearly with pressure but the concentration of ozone does not. This can readily be allowed for by well known software methods.
- Low frequency phase sensitive detection might allow determination of relaxation time and the information can be processed to give improved sensitivity.
- FIG. 3 a shows the response to 20 seconds in the dark and 30 seconds of photolysis starting with initial gas concentrations of 30 ppb NO 2 , 10 ppb NO and 50 ppb O 3 .
- FIG. 3 b shows the equivalent situation starting with 30 ppb NO 2 , 10 ppb NO and 0.5 ppb O 3 .
- FIGS. 3 c and 3 d show the equivalent ozone and nitrogen dioxide concentrations with time for starting concentrations 30 ppb NO 2 , 0.5 ppb NO, 0.5 ppb O 3 ( 3 ( c )) and 300 ppb NO 2 , 0.5 ppb NO, 0.5 ppb O 3 ( 3 ( d )).
- FIGS. 4 ( a ) and 4 ( b ) shows the ozone, nitrogen monoxide and nitrogen dioxide traces with time in response to repeating patterns of 40 seconds in the dark and 40 seconds of photolysis.
- the starting concentrations are 90 ppb NO 2 , 30 ppb NO and 50 ppb O 3 .
- the starting concentrations are 10 ppb NO 2 , 30 ppb NO and 50 ppb O 3 .
- the starting concentrations are 30 ppb NO 2 , 10 ppb NO and 50 ppb O 3
- FIG. 4( d ) shows the corresponding situation for a periodicity of 20 seconds in the dark then 20 seconds photolysis.
- Ozone levels can be monitored throughout the reaction to give a time course or, alternatively, the ultraviolet light source can be pulsed for different durations and individual readings taken after each duration pulse then used to form the equivalent time course.
- This system can therefore readily establish the concentrations of nitrogen monoxide, nitrogen dioxide and ozone concentrations without needing to pre-treat the sample or wait for a steady state to be reached.
- Oxygen is essentially constant and in excess.
- Prior art methodology measures only a steady state ozone concentration after prolonged irradiation and requires two gases to be scrubbed to make the calculation possible. However, by making three or more independent measurements in different conditions, all three gases can be established without having to scrub the input gas sample.
- Examples of suitable ultraviolet sources 4 would be a fluorescent xenon tube, mercury lamp, deuterium lamp, sunlight (perhaps focused through a lens into a reflective cavity), frequency doubled laser or future ultraviolet light source. Indeed, a violet/ultraviolet light emitting diode/diode laser would be ideal if practical devices of this type become available. An ultraviolet light photosensor may be provided to quantify ultraviolet light produced.
- ozone sensor Several different types of ozone sensor would suitable.
- the amperometric type using an aqueous electrolyte and operating at room temperature can be obtained from EN-SCI Inc of Boulder, Colo., USA and City Technology Ltd of Portsmouth, UK.
- Solid state semiconductor sensors with a resistance which changes when exposed to ozone could be used. These operate around 500° C. and examples include the LGL52 Ozone sensor from Capteur Ltd of Didcot, UK. Stain tubes which change color when exposed to ozone may be used. These indicate ozone concentration through the depth to which a color change occurs but are not particularly accurate.
- Such devices can be obtained from Dragerwerk GmbH in Lubeck, Germany.
- Other possible ozone sensors include In 2 O 3 coated surface acoustic wave devices and phthalocyanines.
- Non-aqueous electrolyte amperometric ozone sensors are available from Sensoric GmbH in Bonn, Germany.
- nitrogen dioxide or monoxide might be measured instead by means of a suitable sensor.
- a suitable sensor for example, amperometric nitrogen monoxide and nitrogen dioxide sensors which operate at room temperature are sold by City Technology of Portsmouth, UK.
- the equilibrium between nitrogen monoxide and nitrogen dioxide may be altered by other equilibrium altering means. Therefore, instead of or combined with an ultraviolet light source, there may be provided any other means for affecting the equilibrium between nitrogen dioxide and nitrogen monoxide.
- nitrogen dioxide, nitrogen monoxide or ozone could be added by a gas source or removed by a scrubber. Nitrogen dioxide, nitrogen monoxide or ozone could undergo a chemical reaction, including for example conversion of nitrogen dioxide to nitrogen monoxide using a heated coil, e.g. of platinum/rhodium.
- Temperature and pressure can also affect the equilibrium and these can be varied to give different treatments of the gas sample and therefore measurements of equilibrium with different values of J and k 1 .
- the different position of the equilibrium and/or different characteristic relaxation time under different conditions provides further independent measurements which can be used to calculate all three gas concentrations.
- a sensing apparatus 101 is configured to be attached to a weather balloon (not shown) so that, in use, it can be drawn up through the atmosphere by the weather balloon.
- the arrow in the diagram indicates the direction of air flow through the sensing apparatus 101 when in use.
- the sensing apparatus 101 has a gas conducting member 102 which has a shape such that its diameter in its central portion is less than that at either of its ends.
- Such a configuration generates, in use, a region of low pressure in the central narrow region of the gas conducting member 102 by the well-known Venturi effect. It will be recognised by one skilled in the art that many configurations of gas conducting member 102 would provide said region of low pressure, although an elongate pipe is preferred, particularly broadly cylindrical hourglass-shaped pipe.
- the central region there is positioned a sensor element 103 and a shield member 104 which protects the sensor element 103 from damage due to hailstones, heavy rain, etc during use.
- the shield 104 is arranged such that it connects to the central region of the gas conducting member 102 .
- the low pressure region generated in the gas conducting member 102 draws air into the shield 104 and over the sensor element 103 using, for example, King's Law.
- the sensor element 103 is an ozone detector but it is also possible to detect other atmospheric matter.
- the shield member 104 maybe connected directly to the external outlet 7 of the sensor shown in FIG. 1 but this sensing apparatus 100 may be used with any type of sensor element 103 for detection of different gases.
- FIG. 7 shows an example of a gas conducting member which provides such a high pressure region. Components corresponding to those in FIG. 5 are numbered identically.
- a constricting member is provided at what is, in use, the lower end of gas conducting member 102 .
- the constriction has a narrow opening 108 and tapered base to allow particles such as rain and ice to fall out of the cylindrical member 102 , but is narrow enough to direct air through the shield 104 and over sensor 103 .
- Other configurations of gas conducting member to provide low or high pressure regions will now be apparent to one skilled in the art.
- FIG. 8 shows a detail of a sensor element 103 in a shield 104 .
- the air flow over the sensor element 103 may be generated by a device shown in FIGS. 5 to 7 or by more conventional positioning of the sensor element within a known sensor manifold. It does, however, have particular benefits in the configuration shown in FIGS. 5 to 7 .
- Some sensor elements particularly tungsten oxide detectors for ozone have to be maintained at a high temperature relative to the surrounding air.
- a tungsten oxide sensor will typically be maintained between 500- 600° C. in air which is between 200 and 300° K.
- These sensors are mounted on hot wires and the power supplied to the sensors is altered using standard feedback techniques to maintain sensor element temperature.
- the sensor element 103 is supported by electrical connecting wire 106 which connects to a sensor driving and monitoring device 107 .
- the wires provide electrical energy to a heating element 108 on the sensor 103 or adjacent to the sensor element 103 itself, causing the sensor element 103 to be heated as is standard. Airflow over the sensor element 103 when the sensor 101 is in use cools the sensor element 103 and the actual temperature of the sensor element 103 can be determined by a temperature sensor 109 .
- This air flow data is useful not just to improve the accuracy of readings from the sensor element 103 but also for determining other operating parameters.
Abstract
Description
- This invention relates generally to devices and methods for the detection of atmospheric components and, in particular, to devices and methods for the detection of nitrogen dioxide, nitrogen monoxide and ozone.
- In recent years, with increased concern over environmental issues, there is more and more need for accurate and cost effective measurement devices and methods for the detection of gases in the atmosphere. There is a demand both for measurements of pollutant gases at ground level, due to their direct effect on human health, and also within the atmosphere for atmospheric analysis and research.
- Ozone, nitrogen dioxide and nitrogen monoxide are gases of particular relevance and it is desirable to monitor concentrations of these gases in air. Particular applications include roadside monitoring and atmosphere content monitoring.
- The paper “Indirect Determination of Nitrogen Oxides by Chemiluminescence Techniques” (R. Guicherit, Atmos Environ. 1972 Nov; 6(11) p.807-14) shows a method and apparatus for determining nitrogen dioxide in air samples. This process involves use of a chemiluminescent detection system for ozone, which is produced by means of the effect of ultraviolet light on the equilibrium reaction:
- NO2+O2⇄NO+O3
- Ultraviolet light pushes the equilibrium to the right, forming nitrogen monoxide and ozone. This process involves irradiating a gas sample with ultraviolet light and then determining the final ozone concentration.
- The resulting system is complex and the authors found it essential to pass incoming gas through scrubbers to remove ozone and to oxidise nitrogen monoxide to nitrogen dioxide before beginning irradiation.
- This system further proposed that, once nitrogen dioxide had been determined, the concentration of nitrogen monoxide could subsequently be calculated after a separate reading of ozone produced by ultraviolet irradiation of a separate gas sample, scrubbed as before, with the addition of a further scrubber to remove ozone.
- Another known technique for determining total nitrogen oxide content in air is described in U.S. Pat. No. 3,973,914 to van Heusden. This functions by converting nitrogen dioxide to nitrogen monoxide which is then determined by monitoring chemiluminescence of the reaction between nitrogen monoxide and excess ozone.
- This process is the basis of a number of gas monitoring devices on sale at the present time. However, these devices are expensive (in the order of £10,000), complex and suffer from limitations, particularly relating to the quantitative conversion of nitrogen dioxide to nitrogen monoxide.
- A first aim of the present invention is to provide a cheaper, simpler and more reliable gas monitoring device, capable of accurate determination of nitrogen dioxide, nitrogen monoxide and/or ozone in air.
- One use for a cheaper, simple and more reliable gas monitoring device would be for measuring atmospheric composition at high altitudes. Typically, this is carried out by attaching sensors to a helium filled weather balloon and to launch the balloon into the atmosphere. The sensor then transmits data, usually via a radio link, as the balloon passes up through the atmosphere. The fact that the sensor is attached to a balloon places severe restrictions in terms of weight and cost on the sensor design. The cost aspect can be particularly critical, because generally such sensors have to be treated as disposable, given that they may be difficult to locate once they fall back to the ground. All of this can make it extremely difficult to produce a sensor which provides appropriately accurate readings that are continuous throughout the ascent of the balloon and which is capable of resisting the effects of high altitude and low temperature, where contaminants such as rain ice can affect sensor output.
- Therefore, a second aim of the present invention is to provide a device that is suitably reliable, cheap and light to benefit high altitude gas monitoring.
- Furthermore, high altitude gas measurement systems usually use a pump to draw air into a sensing arrangement. The pumps are expensive, relatively heavy and require considerable power to operate, increasing overall device weight.
- Furthermore, with such sensors it can often be difficult to provide accurate readings because it is difficult to determine exactly the rate at which atmospheric air is flowing over the sensor and a further aim of the present invention is to provide sensing apparatus which mitigates this problem.
- According to a first aspect of the present invention, there is provided an instrument for assaying the concentration of one or more of nitrogen dioxide, nitrogen monoxide and/or ozone in an air sample; the instrument comprising an equilibrium altering means for changing, or an element adapted to change, the equilibrium between nitrogen monoxide and nitrogen dioxide in the presence of ozone and oxygen, and a first gas sensor for quantifying the concentration of a first gas, being one of nitrogen dioxide, nitrogen monoxide or ozone; the instrument being adapted to measure the concentration of the first gas whilst the equilibrium between nitrogen monoxide and nitrogen dioxide in the presence of ozone and oxygen is altered and thereby to calculate the concentration of nitrogen dioxide, nitrogen monoxide and/or ozone in the air sample.
- Preferably, the equilibrium altering means comprises an ultraviolet light source. More preferably, the ultraviolet light source is switched on and off periodically.
- The equilibrium altering means may comprise a means for adding, or an element adapted to add, one or more of nitrogen monoxide, nitrogen dioxide or ozone, and/or a means for removing, or an element adapted to remove, one or more of nitrogen monoxide, nitrogen dioxide, ozone or oxygen.
- Preferably, the instrument is adapted to measure the concentration of the first gas at a plurality of time points and thereby monitor the rate at which the balance between nitrogen dioxide and nitrogen monoxide changes in response to the effects of the equilibrium altering means.
- Typically, the first gas sensor is an ozone sensor.
- The instrument may be adapted to allow for the effects of temperature and/or pressure on the equilibrium between nitrogen dioxide and nitrogen monoxide.
- According to a second aspect of the present invention there is provided a method of calculating the concentration of nitrogen dioxide, nitrogen monoxide and/or ozone in air, the method comprising the steps of:
- activating an equilibrium altering means for changing, or an element adapted to change, the equilibrium between nitrogen monoxide and nitrogen dioxide in the presence of ozone and oxygen in an air sample;
- taking three or more readings of the concentration of a first gas, being one of nitrogen dioxide, nitrogen monoxide or ozone including at least one reading taken before the changes caused by the equilibrium altering means reach a steady state; and
- thereby calculating the concentration of nitrogen dioxide, nitrogen monoxide and/or ozone in the air sample.
- Preferably, the equilibrium altering means is an ultraviolet light source.
- Preferably, the method includes the step of switching the ultraviolet source on and off periodically.
- The equilibrium altering means may comprise a means for adding, or an element adapted to add, one or more of nitrogen monoxide, nitrogen dioxide or ozone.
- The equilibrium altering means may comprise a means for removing, or an element adapted to remove, one or more of nitrogen monoxide, nitrogen dioxide, ozone or oxygen.
- The concentration of the first gas at a plurality of time points may be used to calculate the rate at which the balance between nitrogen dioxide and nitrogen monoxide changes in response to the effects of the equilibrium altering means.
- The readings may be of ozone concentration.
- The method may further include the step of allowing for the effects of temperature and/or pressure on the equilibrium between nitrogen dioxide and nitrogen monoxide.
- According to a third aspect of the present invention there is provided a computer program comprising program instructions which, when loaded onto a computer, are adapted to calculate, or constitute a processing means for calculating, the concentration of nitrogen monoxide, nitrogen dioxide and/or ozone in an air sample by the method of the second embodiment.
- According to a fourth aspect of the present invention there is provided a computer program according to the third aspect embodied on a record medium.
- According to a fifth aspect of the present invention there is provided sensing apparatus for detecting components in atmospheric air as the sensor is drawn up through the atmosphere, the sensor comprising:
- a sensor element;
- shielding means for shielding, or an element adapted to shield, the sensor element from direct contact with air flow as the sensor is drawn through the atmosphere; and
- means for diverting, or an element adapted to divert, air through the shielding means and over the sensor element as the sensor passes through the atmosphere.
- Preferably, the means for diverting air comprises a gas conducting member shaped to provide a pressure differential across the shielding means and cause air to move through the shielding means.
- The gas conducting member may be shaped to provide a low pressure region at an entry to the shielding means and thereby draw air through the shielding means into the gas conducting member.
- The gas conducting member may comprise a flow restricting member for diverting air that flows through the gas conducting member in use into the shielding means.
- The sensing apparatus may have an aperture to allow water or ice to flow out of the gas conducting member.
- According to a sixth aspect of the present invention there is provided sensing apparatus comprising:
- a sensor element;
- means for regulating, or an element adapted to regulate, the temperature of the sensor element by providing heat energy to the sensor element; and
- means for calculating the air flow across the sensor element from the amount of heat energy supplied to the sensor element.
- The sensor apparatus may further comprise a means for measuring, or an element adapted to measure, the temperature of the sensor.
- Examples of the present invention will now be described with reference to the accompanying drawings, in which:
- FIG. 1 is a schematic diagram of an analytical system according to the present invention;
- FIG. 2 shows the response with time of ozone concentration in response to periodic ultraviolet irradiation, J;
- FIG. 3 shows the simulated variation of ozone, nitrogen monoxide and nitrogen dioxide concentrations in response to specific changes to the level of ultraviolet irradiation;
- FIG. 4 shows the simulated variation of ozone, nitrogen monoxide and nitrogen dioxide concentrations in response to specific periodic changes to the level of ultraviolet irradiation;
- FIG. 5 is a schematic cross-section through an example sensing apparatus;
- FIG. 6 is an expanded view of a section of FIG. 5;
- FIG. 7 is a schematic cross-section through an alternative sensing apparatus; and
- FIG. 8 is a schematic cross-section through a further sensing apparatus.
- FIG. 1 shows an example analytical system according to the present invention. The analytical system shown generally as1 comprises an
air inlet 2 which allows an air sample to enterirradiation chamber 3. Theirradiation chamber 3 comprises anultraviolet source 4 and may be encased by an ultravioletreflective surface 13 such as a metal foil. There is achamber outlet 5 from the irradiation chamber, which incorporates aUV light trap 6. Air passes from thechamber outlet 5 to an external outlet 7 via anozone sensor 10. A pump (not shown) or airflow control means as discussed below may be provided to draw air through the external outlet 7 and through the sensor as a whole. - Within the irradiation chamber, ultraviolet light from the
ultraviolet source 4 irradiates the air sample, driving the below reaction towards the formation of ozone and nitrogen monoxide: - NO2+O2⇄NO+O3
- By positioning an
ozone sensor 10 downstream from theultraviolet source 4, readings can be taken of ozone levels after the equilibrium has been affected by irradiation (or other means discussed below). - A processing means20 such as a computer, microprocessor or other device having storage and processing capacity is provided to analyse the measurements and compute gas concentrations in the input gas sample. The invention further extends to the software used by said processing means 20 to control the switching on and off of the ultraviolet light source, record gas concentration readings from the
sensor 10 and carry out gas concentration calculations. Said software may be provided on a digital storage means such as a magnetic or optical disk or solid state storage device such as EEPROM. - The basis of the present invention is that readings of ozone concentration are taken not simply after the ratio of nitrogen monoxide to nitrogen dioxide has been modified by the influence of ultraviolet light or other factors and a steady state has been reached, but also either (a) during the process of this ratio being altered or (b) after or during the application of two different means for altering the ratio. The resulting readings are then used to calculate the concentrations of nitrogen monoxide, nitrogen dioxide and ozone in the gas sample.
-
- where [O3] is the instantaneous concentration of ozone, [NO2] is the instantaneous concentration of nitrogen dioxide, [NO] is the instantaneous concentration of nitrogen monoxide, J1 is rate coefficient for photolysis of NO2, in units of per second, and k2 is the rate constant for the reverse reaction.
- At equilibrium steady state:
- [O3 ]=J 1[NO2 ]/k 2 [NO]
- Characteristic time, τ, to equilibrium is given by:
- τ=(J 1 +k 2[NO])−1
- Both equilibrium steady state ozone concentration and characteristic time can be readily deduced either from monitoring the ozone concentration curve with time or from several individual ozone readings at different times by well-known mathematical methods.
- Case 1: in the sunlit atmosphere:
- Typically[O3]=50 ppb—in excess over NO
- J1=Jsunlight (=10−2 s−1)
- τ=(10−2+5×10−4 [NO] (ppb))−1 s,
- and so τ<100 secs
- Case 2: in the instrument under photolysis:
- J1=JNO2 (=0.1 s−1)
- τ=(10−1+5×10−4 [NO])1
- and so τ<10 secs
- Case 3: in the dark:
- J1=0
- Therefore, in the dark, the atmospheric steady state relaxes towards a state where [NO] (or O3) tends to zero with τ=(5×10−4 [NO])−1 or (5×10−4 [O3])−1 depending on which gas is present in excess. Therefore, typically τ>(2.5×10−2)−1>40 secs. If, however, concentrations of [NO] and [O3] are similar, it will be clear to one skilled in the art that you instead get a complex but mathematically definable rate of ozone loss.
- By monitoring the ozone concentration in response to periodic light and dark and application of standard computing techniques it is therefore possible to get information about all three components [O3], [NO2] and [NO].
- In a preferred embodiment, light is pulsed as shown in FIG. 2 which illustrates the periodic alteration of J with time and the resulting ozone concentration. Clearly the precise pulse shape of ozone concentration will depend on the gas flow rate, length of the ultraviolet irradiation zone, spectrum and intensity of ultraviolet source, gap between the end of irradiation zone and sensor and other calculable parameters.
- Therefore, d[O3]/dt under instrument irradiation can be used to give the concentration of nitrogen dioxide in the air sample.
- Measurement of ozone concentration after short sample time in dark gives the ozone concentration in the air sample.
- The concentration of ozone after full relaxation in the dark gives the difference between sample ozone and nitrogen monoxide concentrations.
- The characteristic relaxation time in the dark of an unphotolysed air sample gives the nitrogen monoxide concentration.
- The characteristic relaxation time of a photolysed air sample gives the sum of the concentrations of nitrogen monoxide and nitrogen dioxide.
- The time resolved measurement of ozone therefore allows rates and relaxation time to be determined and so the concentrations of nitrogen monoxide, nitrogen dioxide and ozone can be determined. Temperature has an effect on the value of J1. The corresponding chemical step has a small activation energy thus temperature effects are small. If temperature effects need to be corrected this can be done using a simple measurement of temperature from a temperature measuring means (not shown). Pressure will have a still smaller effect and will preferably not be taken into account; however, it could be readily corrected for if required using readings from a pressure gauge (not shown). Pressure has a linear effect on the measured concentration for some types of ozone sensor as the partial pressure of ozone changes linearly with pressure but the concentration of ozone does not. This can readily be allowed for by well known software methods.
- Low frequency phase sensitive detection might allow determination of relaxation time and the information can be processed to give improved sensitivity.
- FIG. 3 and4 show the concentration of nitrogen monoxide, nitrogen dioxide and ozone with time (in seconds) for various simulated experiments at 298 Kelvin, 1 atmosphere pressure, k=0.06 per second.
-
- O3+NO →NO2+O2
- FIG. 3a shows the response to 20 seconds in the dark and 30 seconds of photolysis starting with initial gas concentrations of 30 ppb NO2, 10 ppb NO and 50 ppb O3.
- FIG. 3b shows the equivalent situation starting with 30 ppb NO2, 10 ppb NO and 0.5 ppb O3.
- FIGS. 3c and 3 d show the equivalent ozone and nitrogen dioxide concentrations with time for starting
concentrations 30 ppb NO2, 0.5 ppb NO, 0.5 ppb O3 (3(c)) and 300 ppb NO2, 0.5 ppb NO, 0.5 ppb O3(3(d)). - FIGS.4(a) and 4(b) shows the ozone, nitrogen monoxide and nitrogen dioxide traces with time in response to repeating patterns of 40 seconds in the dark and 40 seconds of photolysis. In the case of FIG. 4(a), the starting concentrations are 90 ppb NO2, 30 ppb NO and 50 ppb O3. In the case of FIG. 4(b) the starting concentrations are 10 ppb NO2, 30 ppb NO and 50 ppb O3. In FIG. 4(c) the starting concentrations are 30 ppb NO2, 10 ppb NO and 50 ppb O3, FIG. 4(d) shows the corresponding situation for a periodicity of 20 seconds in the dark then 20 seconds photolysis.
- Ozone levels can be monitored throughout the reaction to give a time course or, alternatively, the ultraviolet light source can be pulsed for different durations and individual readings taken after each duration pulse then used to form the equivalent time course.
- This system can therefore readily establish the concentrations of nitrogen monoxide, nitrogen dioxide and ozone concentrations without needing to pre-treat the sample or wait for a steady state to be reached. (Oxygen is essentially constant and in excess). Prior art methodology measures only a steady state ozone concentration after prolonged irradiation and requires two gases to be scrubbed to make the calculation possible. However, by making three or more independent measurements in different conditions, all three gases can be established without having to scrub the input gas sample.
- Examples of suitable
ultraviolet sources 4 would be a fluorescent xenon tube, mercury lamp, deuterium lamp, sunlight (perhaps focused through a lens into a reflective cavity), frequency doubled laser or future ultraviolet light source. Indeed, a violet/ultraviolet light emitting diode/diode laser would be ideal if practical devices of this type become available. An ultraviolet light photosensor may be provided to quantify ultraviolet light produced. - Several different types of ozone sensor would suitable. For example, the amperometric type using an aqueous electrolyte and operating at room temperature. Such sensors can be obtained from EN-SCI Inc of Boulder, Colo., USA and City Technology Ltd of Portsmouth, UK. Solid state semiconductor sensors with a resistance which changes when exposed to ozone could be used. These operate around 500° C. and examples include the LGL52 Ozone sensor from Capteur Ltd of Didcot, UK. Stain tubes which change color when exposed to ozone may be used. These indicate ozone concentration through the depth to which a color change occurs but are not particularly accurate. Such devices can be obtained from Dragerwerk GmbH in Lubeck, Germany. Other possible ozone sensors include In2O3 coated surface acoustic wave devices and phthalocyanines. Non-aqueous electrolyte amperometric ozone sensors are available from Sensoric GmbH in Bonn, Germany.
- In an alternative embodiment, nitrogen dioxide or monoxide might be measured instead by means of a suitable sensor. For example, amperometric nitrogen monoxide and nitrogen dioxide sensors which operate at room temperature are sold by City Technology of Portsmouth, UK.
- It will be clear to one skilled in the art that an air sample could be trapped in a volume, irradiated and then monitored in situ; however, it is preferred to maintain a flow of air.
- In an alternative embodiment, instead of altering the length of time for which a gas sample is irradiated, the equilibrium between nitrogen monoxide and nitrogen dioxide may be altered by other equilibrium altering means. Therefore, instead of or combined with an ultraviolet light source, there may be provided any other means for affecting the equilibrium between nitrogen dioxide and nitrogen monoxide. For example, nitrogen dioxide, nitrogen monoxide or ozone could be added by a gas source or removed by a scrubber. Nitrogen dioxide, nitrogen monoxide or ozone could undergo a chemical reaction, including for example conversion of nitrogen dioxide to nitrogen monoxide using a heated coil, e.g. of platinum/rhodium. Temperature and pressure, can also affect the equilibrium and these can be varied to give different treatments of the gas sample and therefore measurements of equilibrium with different values of J and k1. The different position of the equilibrium and/or different characteristic relaxation time under different conditions provides further independent measurements which can be used to calculate all three gas concentrations.
- Although calculations are shown which involve the intermediate step of calculating equilibrium steady state concentration of ozone and characteristic time to equilibrium, it will be immediately clear to one skilled in the art that equivalent mathematical calculations may be used to give the required sample gas concentrations and a particular method of calculation can be selected by one skilled in the art.
- It may further be taken into account in the calculations that incoming nitrogen monoxide and nitrogen dioxide will be in equilibrium already, although this depends on the ambient ultraviolet level. Given that air oxygen is present in a constant excess (albeit one which varies with altitude) this further constraint could improve the accuracy of the calculations. In this case an external ultraviolet light photosensor might be used to quantify the level of ultraviolet light experienced externally by the gas sample.
- Further sensors, such as an ozone sensor (not shown) besides the
inlet 2 may allow further accuracy, although this is not required in the present invention. - It will be clear that a controlled rate of gas flow through the sensor is important. In weather balloons, the weight of a conventional pump is prohibitive.
- Referring to FIG. 5, a sensing apparatus101 according to the invention is configured to be attached to a weather balloon (not shown) so that, in use, it can be drawn up through the atmosphere by the weather balloon. The arrow in the diagram indicates the direction of air flow through the sensing apparatus 101 when in use. The sensing apparatus 101 has a
gas conducting member 102 which has a shape such that its diameter in its central portion is less than that at either of its ends. Such a configuration generates, in use, a region of low pressure in the central narrow region of thegas conducting member 102 by the well-known Venturi effect. It will be recognised by one skilled in the art that many configurations ofgas conducting member 102 would provide said region of low pressure, although an elongate pipe is preferred, particularly broadly cylindrical hourglass-shaped pipe. - In the central region there is positioned a
sensor element 103 and ashield member 104 which protects thesensor element 103 from damage due to hailstones, heavy rain, etc during use. Theshield 104 is arranged such that it connects to the central region of thegas conducting member 102. In use, the low pressure region generated in thegas conducting member 102 draws air into theshield 104 and over thesensor element 103 using, for example, King's Law. In this example thesensor element 103 is an ozone detector but it is also possible to detect other atmospheric matter. - The
shield member 104 maybe connected directly to the external outlet 7 of the sensor shown in FIG. 1 but thissensing apparatus 100 may be used with any type ofsensor element 103 for detection of different gases. - Instead of using a low pressure region to draw air through the
shield 104, the invention also encompasses the use of a high pressure region to drive air through theshield 104 and past thesensor element 103. FIG. 7 shows an example of a gas conducting member which provides such a high pressure region. Components corresponding to those in FIG. 5 are numbered identically. In this example a constricting member is provided at what is, in use, the lower end ofgas conducting member 102. The constriction has a narrow opening 108 and tapered base to allow particles such as rain and ice to fall out of thecylindrical member 102, but is narrow enough to direct air through theshield 104 and oversensor 103. Other configurations of gas conducting member to provide low or high pressure regions will now be apparent to one skilled in the art. - FIG. 8 shows a detail of a
sensor element 103 in ashield 104. In this example the air flow over thesensor element 103 may be generated by a device shown in FIGS. 5 to 7 or by more conventional positioning of the sensor element within a known sensor manifold. It does, however, have particular benefits in the configuration shown in FIGS. 5 to 7. - Many sensors elements are sensitive to air flow and it is important to know to be able to either fix or measure the air flow past such sensors. It is desirable to do this in such a fashion as to minimise the number, cost and weight of instruments and apparatus.
- Some sensor elements, particularly tungsten oxide detectors for ozone have to be maintained at a high temperature relative to the surrounding air. For example, a tungsten oxide sensor will typically be maintained between 500- 600° C. in air which is between 200 and 300° K. These sensors are mounted on hot wires and the power supplied to the sensors is altered using standard feedback techniques to maintain sensor element temperature.
- In this example, the
sensor element 103 is supported by electrical connectingwire 106 which connects to a sensor driving andmonitoring device 107. The wires provide electrical energy to a heating element 108 on thesensor 103 or adjacent to thesensor element 103 itself, causing thesensor element 103 to be heated as is standard. Airflow over thesensor element 103 when the sensor 101 is in use cools thesensor element 103 and the actual temperature of thesensor element 103 can be determined by atemperature sensor 109. - However, as the primary source of cooling of the
sensor element 103 is the passing air and as this depends in a calculable relationship on the speed of the passing air, this invention recognises that the amount of power required to maintain the temperature of the sensor can be used to calculate the rate of cooling of the sensor due to passing air and therefore the speed of said passing air. - This air flow data is useful not just to improve the accuracy of readings from the
sensor element 103 but also for determining other operating parameters. - Further alterations and modifications may be made within the scope of the invention herein disclosed. Accordingly, the scope of the present invention should be construed solely by reference to the appended claims.
Claims (32)
Priority Applications (1)
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US10/889,824 US7323343B2 (en) | 2000-01-28 | 2004-07-13 | Nitrogen monoxide, nitrogen dioxide and ozone determination in air |
Applications Claiming Priority (2)
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GBGB0002081.8A GB0002081D0 (en) | 2000-01-28 | 2000-01-28 | Atmospheric content detection |
GBGB0002081.8 | 2000-01-28 |
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US10/889,824 Continuation US7323343B2 (en) | 2000-01-28 | 2004-07-13 | Nitrogen monoxide, nitrogen dioxide and ozone determination in air |
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US09/774,157 Abandoned US20010042843A1 (en) | 2000-01-28 | 2001-01-29 | Air content determination |
US10/889,824 Expired - Fee Related US7323343B2 (en) | 2000-01-28 | 2004-07-13 | Nitrogen monoxide, nitrogen dioxide and ozone determination in air |
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Also Published As
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EP1120649A3 (en) | 2005-11-02 |
GB0002081D0 (en) | 2000-03-22 |
EP1120649A2 (en) | 2001-08-01 |
US7323343B2 (en) | 2008-01-29 |
US20040241868A1 (en) | 2004-12-02 |
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