The present invention relates to systems for measuring minute concentrations of constituents dissolved in liquids, and more particularly to systems that employ analyte separation and aerosol generation to distinguish constituents and measure their concentrations.
A variety of instruments are used for identifying and measuring concentrations of solutes in liquid media. Separators can employ any one of several analyte separation techniques, e.g. liquid chromatography, high performance liquid chromatography (normal or reversed phase), ion exchange chromatography and gel permeation chromatography. Analyte separation involves moving liquid and dissolved constituents, known as the mobile phase, through a stationary phase, e.g. a stainless steel column or tube packed with 5-10 mm silicon beads. As the liquid passes through the column, different analytes become separated from one another due to differing rates at which they travel through the stationary phase. The liquid leaving the stationary phase is comprised of spatially separated concentrations of the individual analytes. As a result, a continuous measurement of the liquid stream yields a chromatogram in which indications of relatively high concentration are temporally separated from one another to suggest the presence of different analytes. The chromatogram corresponds to the physical separation of the analytes at the column exit, by recording the different times at which different analyte concentrations leave the column. The exit times are useful in identifying the analytes involved.
Among the techniques for measuring analyte concentrations, several involve generating aerosols based on the mobile phase exiting the column. In one of these, known as evaporative light scattering, a nebulizer is used to generate droplets of the solution eluting from the separator column. The droplets dry as they are carried by air or another gas, forming a stream of non-volatile residue particles. As the particles are moved past a laser beam, each particle that intersects the beam scatters light, with larger particles scattering light at higher intensity. Thus, the amplitude of a photodetector output provides a measurement of particle size, which in turn provides an indication of analyte concentration.
To enhance measurement of small analyte concentrations, the particle stream can be directed through a condensation particle counter (CPC), in which the particles travel through a region saturated with the vapor of a working medium that condenses onto the non-volatile residue particles that exceed a threshold diameter, “growing” each particle into a considerably larger droplet that is more easily detected by optical means.
In another technique, known as evaporative electrical detection, the solution leaving a separator column is nebulized to provide an aerosol stream, with the droplets again dried to provide a particle stream. The particle stream is brought into a confluence with a stream of ions, to apply a size-dependent electrical charge to the non-volatile residue particles. An electrically conductive filter collects the particles and generates an electrical current indicative of analyte concentration.
While the systems are well suited for a variety of applications, they are subject to difficulties that limit their utility. One of these is the lack of sensitivity sufficient for detecting and measuring extremely low analyte concentrations. As environmental standards for exposure to various contaminants become more stringent, and as product testing and manufacturing techniques are directed to applications that require more accurate measurement of constituents or have a reduced tolerance to certain constituents, there is an ever increasing need to measure smaller amounts of analytes with accuracy.
Another difficulty concerns bubble formation due to gasses dissolved in the water or other liquid entering the nebulizer. Bubbles can be formed when the liquid flow rate is below the natural aspiration rate, with the liquid drawn into the nebulizer at a pressure below atmospheric pressure. The bubbles eventually break free and tend to disrupt residue concentration measurements downstream of the nebulizer.
A further system problem, relating to the condensation particle counter, concerns the use of butyl alcohol or similar fluids with low vapor mass diffusivity for growing the residue particles into droplets. Such liquids tend to be flammable, toxic, and produce noxious odors. Frequently they are subject to health and environmental regulations that restrict their use in indoor environments. In addition, the liquids require equipment for supplying, collecting and recirculating the liquid involved, and in some cases for separating the liquid from water.
Another persistent problem, due to relatively long fluid flow paths within and between the nebulizer and CPC, is the relatively long time elapsed between a change in the concentrations of analytes in a given liquid sample, and the detection of the change. The longer paths allow more time for axial diffusion, which ultimately has a negative impact on the instrument response.
Another difficulty with conventional condensation particle counters is the limited dynamic range typical of many CPC designs, due primarily to the increase in coincidence events that accompanies increased particle concentration.
Accordingly the present invention has several aspects, directed to one or more of the following objects:
In general, the invention is drawn to a system for analyzing liquid samples including an analyte separator, an aerosol generator for producing an aerosol stream of suspended particles derived from the liquid output of the separator, and a particle sensing device responsive to the particles for measuring analyte concentrations.
One aspect of the invention is a system for measuring analyte concentrations in liquids. The system includes an analyte separation stage adapted to separate different analytes in a liquid sample primarily into different regions within the liquid sample. This produces a separation stage output in which a plurality of different analytes are so separated. A nebulizing stage, downstream of the analyte separation stage, is adapted to generate an aerosol stream composed of droplets of the separation stage output suspended in a carrier gas. An evaporation stage, downstream of the nebulizing stage, is adapted to substantially evaporate the liquid whereby the aerosol leaving the evaporation stage is composed of residue particles of the different analytes suspended in the carrier gas. A saturation stage, disposed downstream of the evaporation stage, is maintained substantially at a first temperature, and adapted to merge the aerosol with a working medium vapor having a mass diffusivity higher than a thermal diffusivity of the carrier gas, to substantially saturate the aerosol with the working medium vapor. A condensation stage, disposed downstream of the saturation stage, is maintained at a second temperature above the first temperature, and adapted to merge further working medium vapor with the substantially saturated aerosol to supersaturate the aerosol and thereby cause droplet growth through condensation of the working medium onto the residue particles. A sensing stage, downstream of the condensation stage, is adapted to optically sense the droplets and generate electrical signals useful in indicating analyte concentrations.
In preferred systems, the saturation stage, condensation stage and sensing stage are provided by a condensation particle counter (CPC). These systems can use water, whose vapor has a relatively high mass diffusivity, as the working or condensing medium. Using water avoids the health and environmental concerns associated with butyl alcohol and other perflourinated hydrocarbons. This eliminates the need to supply, store and recover such fluids, and to separate such fluids from the water.
When water is used as the working medium, the aerosol stream is saturated with water vapor and proceeds to a condensing region surrounded by wetted walls that are heated to provide a temperature higher than that of the saturated aerosol stream. Maximum supersaturation occurs at the center of the aerosol flow, given that the water vapor and heat both travel radially inward, and the mass diffusivity of water exceeds the thermal diffusivity of air.
One advantage of using water as the working fluid in the CPC is a substantially higher threshold at which spontaneous nucleation (also called homogeneous nucleation) occurs, compared to a CPC in which working medium is butyl alcohol. An improved coincidence correction process also contributes to a considerably higher permitted particle throughput rate. As a result of these advantages, the concentration information is available virtually in real time, and can encompass concentrations ranging from a single part per trillion to ten parts per million in the single count mode. If desired, a photometric mode can be employed to increase the upper limit to over one part per thousand.
Another aspect of the invention is a system for analyzing liquids. The system includes an analyte separator adapted to separate different analytes in a liquid sample primarily into different regions within the liquid sample, thereby to produce a separator output in which a plurality of different analytes are so separated. A nebulizer is fluid coupled to receive at least a portion of the separator output, and to generate an aerosol composed of droplets of the liquid suspended in a carrier gas. A conduit structure is provided for guiding travel of the aerosol in an aerosol stream away from a merger zone of the nebulizer. At least a portion of the conduit structure is permeable to the liquid, to promote an evaporation of the liquid and migration of the vapor through that portion of the conduit to an exterior thereof as the aerosol is conveyed along the conduit structure. The aerosol leaving the conduit structure is composed of residue particles of the analytes suspended in the carrier gas. A concentration indicating component is disposed to receive the aerosol leaving the conduit structure, and is adapted to indicate analyte concentrations based on the residue particles received.
The concentration indicating component can comprise a droplet growth component disposed downstream of the conduit structure to receive the aerosol and merge the aerosol and a working medium vapor, to supersaturate the aerosol and thereby cause droplet growth through condensation of the working medium onto the residue particles. In this case, the concentration indicating component further includes a droplet sensing component, downstream of the condensation component, adapted to optically detect the droplets and generate electrical signals indicating analyte concentrations.
The conduit structure can be incorporated into the nebulizer, or can be provided as a length of tubing running between the nebulizer and the droplet growth component, e.g. a condensation particle counter. A preferred material for the tubing or nebulizer interior wall is a copolymer available from E. I. duPont de Nemours and Company of Wilmington, Del. under the brand name “Nafion.” So long as the ambient environment surrounding the tubing or nebulizer is less humid than the aerosol, the liquid evaporates and migrates outwardly through the wall in a process referred to as “perevaporation,” resulting in a rapid drying of the aerosol stream. In addition to water, the Nafion tubing can remove alcohols, amines and ammonia from the aerosol stream. The more rapid removal of vapors can permit a considerably shorter aerosol pathway between the nebulizer and the CPC. A key feature of the Nafion conduit structure is that it facilitates vapor removal at lower temperatures, for improved detection of volatile analytes.
The nebulizer can incorporate a heating element just downstream of the impactor, and an inlet downstream of the heating element for admitting dry air to dilute the aerosol stream and reduce the dew point of the liquid vapor.
Another aspect of the invention is a system for analyzing liquid samples. The system includes an analyte separator adapted to separate analytes in a liquid sample primarily into different regions within the liquid sample, to produce a separator output in which a plurality of different analytes are so separated. A nebulizer is fluid coupled to receive at least a portion of the separator output in a merger zone thereof, to generate an aerosol composed of droplets of the liquid suspended in a carrier gas. An evaporation stage, downstream of the nebulizer, is adapted to substantially evaporate the liquid whereby the aerosol leaving the evaporation stage is composed of residue particles of the different analytes suspended in the carrier gas. An electrostatic selector is disposed downstream of the evaporation stage and adapted to selectively remove, from the aerosol, residue particles having sizes less than a predetermined threshold. A concentration indicating component downstream of the selector is adapted to generate analyte concentration information based on residue particles received from the selector.
The concentration indicating component can comprise an optical particle counter adapted to cause growth of droplets through condensation of a working medium onto the residue particles, then optically sense the resulting droplets to generate indications of analyte concentrations.
In one version of the system, the electrostatic selector comprises a unipolar electrical charging device, e.g. a corona discharge element generating multiple ions to merge with the aerosol and charge the particles. This is followed by an ion trap selectively biased to remove the ions and particles having higher electrical mobilities. In another version of the system, the selector comprises a neutralizer which applies a bipolar charge to the aerosol particles, followed by a differential mobility analyzer (DMA). An aspect of this version is that the DMA can be used to remove residue particles on both sides of a desired range of particle electrical mobilities, in effect setting an upper limit as well as a lower limit for particle retention. Either of these versions can be used to improve the response to volatile analytes. In addition, analyte concentration information can be generated by means other than optical particle counting.
Yet another aspect of the invention is a device for generating an aerosol composed of multiple droplets of a liquid. The device includes a housing forming a mixing chamber having (i) a liquid entrance for receiving a sample liquid into the chamber, (ii) a primary orifice having a first diameter for receiving a pressurized gas into the chamber for merger with the sample liquid to generate an aerosol composed of multiple droplets of the sample liquid suspended in the gas, and (iii) a secondary orifice having a second diameter for conducting the aerosol out of the chamber. The second diameter is less than a major dimension of the mixing chamber taken in a direction substantially perpendicular to an axis of the secondary orifice, so as to restrict flow out of the mixing chamber to generate a back pressure in opposition to entry of the sample liquid and the pressurized gas into the chamber.
In contrast to previous nebulizers in which the chamber exit is simply open to the downstream components with a diameter equal to that of the chamber, the exit orifice in the present nebulizer has a diameter less than that of the chamber, and more preferably less than half the chamber diameter. The diameter reduction provides a constriction which produces a higher kinetic energy mixing of the gas and separator eluent in the merger zone. As a result, the nebulizer generates smaller droplets. The secondary orifice also helps direct the aerosol towards the impactor raising the impactor efficiency
Another factor reducing droplet size is a close axial positioning of an impactor, just downstream of the secondary orifice. The more closely spaced impactor removes a greater proportion of the larger droplets, reducing baseline concentration (noise) for improved dynamic range in generating analyte concentration data.
In a preferred version of the nebulizer, the impactor axial spacing from the secondary orifice is adjustable through movement of the impactor. For example, a threaded mounting of the impactor to the nebulizer frame allows axial position adjustment by turning the impactor about its longitudinal axis. The average size of droplets in the aerosol leaving the nebulizer can be increased or decreased by respectively enlarging or reducing the axial spacing between the secondary orifice and the impactor.
The droplet size also can be adjusted by changing or selecting the secondary orifice. Reducing the diameter of the secondary orifice is believed to increase back pressure and reduce droplet size. It has been found useful to provide a secondary orifice with a diameter larger than that of the primary orifice. The ratio of the secondary orifice diameter to the primary orifice diameter can range from slightly above one, to about two in versions that incorporate a secondary orifice.
A further aspect of the invention is a device for optically detecting fine particles in an aerosol. The device includes a housing having an inlet for receiving an aerosol consisting essentially of substantially dry submicrometer residue particles suspended in a carrier gas, and a passage for conveying the aerosol in a steady stream through the housing along a saturation region and along a supersaturation region downstream of the saturation region. A holding component, disposed along the passage, is adapted to contain a condensing medium in liquid form and to release the condensing medium in vapor form as the aerosol is conveyed along the passage. A first temperature maintenance device, disposed proximate the passage along the saturation region, is adapted to maintain the saturation region substantially at a first temperature. A second temperature maintenance device, disposed proximate the passage along the supersaturation region, is adapted to maintain the supersaturation region substantially at a second temperature different from the first temperature. A controller operably associated with the temperature maintenance devices for selectively setting the first temperature, the second temperature, and a difference between the first and second temperatures, to selectively vary a nucleation threshold at which the particles are capable of serving as nuclei for condensation of the working medium to grow droplets. A droplet detector, disposed at a sensing location downstream of the passage, is adapted to sense the droplets resulting from said condensation as they pass the sensing location.
In detectors (e.g. condensation particle counters) that use working media with mass diffusivities higher than the thermal diffusivity of air or another gas, the controller and temperature maintenance devices are configured to maintain the second temperature within a higher range than that of the first temperature, for a supersaturation region that is warmer than the saturation region. Conversely, in a CPC using lower mass diffusivity media such as butyl alcohol, the first temperature is maintained within the higher range to insure that the supersaturation region is cooler than the saturation region. In either event, the difference between the first and second temperatures can be selectively adjusted to influence droplet nucleation and growth. For example, increasing the difference between the first and second temperatures lowers the nucleation threshold, tending to increase the number of particles sensed and therefore counted.
In another version of the device, the first and second temperature ranges are substantially overlapping, in which case the controller can be used to select either the saturation region or the supersaturation region as the warmer region.
Thus, analyte measuring systems configured according to the present invention generate more reliable concentration information in virtually real time and over a wider range of residue concentrations.
For a further understanding of the above and other features and advantages, reference is made to the following detailed description and to the drawings, in which:
Turning now to the drawings, there is shown in
Beyond valve 22, the carrier liquid (mobile phase) and plugs travel at the predetermined flow rate into a high performance liquid chromatography column 26. Column 26 includes a stainless steel tube loaded with a stationary phase, e.g. silicon beads as noted previously. The liquid sample plugs move through column 26 along with the carrier liquid. As each plug proceeds through the column, different constituents travel through the column at different rates, depending largely on their chemical attraction to the stationary phase as compared to their chemical attraction to the mobile phase. Materials having stronger interaction with the stationary phase tend to travel more slowly, as compared to materials having stronger interactions with the mobile phase. As a result, different constituents tend to become concentrated in different regions of each liquid sample plug as it travels through column 26. Consequently, each plug as it leaves column 26 has distinct regions with different concentrations of different constituents, separated from one another temporally as well as spacially since the with liquid sample is moving at the predetermined flow rate as it leaves the HPLC column.
A conduit 28 transfers either all or a predetermined fraction of the HPLC column output to a pneumatic nebulizer 30. The nebulizer also receives air, nitrogen or another gas under pressure from a pressurized gas source 32. Within nebulizer 30, the liquid sample and compressed gas are merged to generate an aerosol including droplets of the liquid sample suspended in the gas.
Most of the liquid provided to nebulizer 30, over 95 percent and typically closer to 100 percent, is not used to form droplets, but instead is drained from the nebulizer through a waste conduit 33.
The aerosol stream is dried to reduce the aerosol droplets to suspended residue particles. Then the aerosol stream is provided to a condensation particle counter (CPC) 34. As the aerosol travels through the CPC, it is first saturated with water from a working fluid supply 36. Then, the aerosol is channeled through a condensation or supersaturation region in which the residue particles act as nuclei for condensation. The residue particles “grow” into considerably larger droplets that are optically detected and counted to generate non-volatile residue concentration information. The concentration information is provided to a microprocessor 38. The microprocessor provides the information to a video display terminal 40 to generate a continuously updated record of non-volatile residue concentrations in the liquid sample.
CPC 34 includes an exit 44 through which the aerosol is drawn by a pump 120 (
Air from source 32 is provided through a solenoid valve 50 to a regulator 52 and measured using a pressure transducer 54. Downstream, the air passes through a high efficiency particle air (HEPA) filter 56, and then is supplied via an entrance 58 to merger zone 48 at a pressure of 30 psi and a flow rate of 0.6 liters per minute through a conduit 60. Air also is provided to an aerosol conditioning zone 62 of nebulizer 30 through a conduit 64. Conduit 64 includes either a valve or a control orifice 66 for limiting the air flow to a rate of about 2.7 liters per minute.
Nebulizer 30 includes a reservoir 68 in fluid communication with the merger zone. The reservoir collects most of the mobile phase supplied through conduit 28, i.e. the liquid not used to form the aerosol droplets. A pump 70 is coupled to the reservoir for evacuating the waste liquid from nebulizer 30.
With reference to
As best seen in
In one suitable version of nebulizer 30, primary orifice 86 has a diameter of 0.006 inches, and secondary orifice 88 has a diameter of 0.008 inches. The chamber has a diameter of 0.020 inches, and an axial length, i.e. space in between orifice plates 86 and 88, of 0.020 inches.
More generally, the secondary orifice diameter is larger than the primary orifice diameter, yet less than the diameter of the cylindrical chamber. As compared to prior devices in which there is no secondary orifice and the chamber is simply open at the exit end, there is a back pressure due to the secondary orifice which increases the feed pressure to the merger zone and results in a higher kinetic energy mixing of the liquid and compressed gas. This advantageously results in smaller sample liquid droplets in the aerosol leaving the merger zone.
As the size of the secondary orifice is reduced, the droplet size is reduced and the back pressure is increased. When the sample liquid is water, it has been found satisfactory to form the secondary orifice and the primary orifice at a diameter ratio of 2 to 1 as indicated by the diameters given above. For a sample liquid with a boiling point lower than water, the preferred diameter ratio is closer to 1, yet the secondary orifice remains larger than the primary orifice.
The higher energy in the merger zone more effectively breaks up the liquid. The secondary orifice also appears to improve the efficiency of the impactor downstream. The ratios of primary and secondary orifice diameters can be selected to vary the pressure at the liquid entrance to the merger zone, relative to atmospheric pressure. Depending on the diameter ratio, air inlet pressure and liquid flow rate (as determined by the HPLC pump), the liquid pressure can be adjusted from below atmospheric pressure to a pressure nearly equal to the inlet air pressure. Keeping the liquid near atmospheric pressure is advantageous for reducing measurement errors due to outgassing.
As seen in
The droplets impinging upon impactor 80 may remain on the impactor momentarily, but eventually descend to reservoir 68 to be removed from the nebulizer as needed through pump 70. If desired, impactor 80 may be formed of sintered metal to provide a porous structure that more effectively prevents the larger, impacting droplets from interfering with the aerosol flow.
As the aerosol stream proceeds along conditioning zone 62, it is heated by an electrical heating element 92 to a temperature of 35-100° C., depending on the mobile phase and analyte volatility. This evaporates the sample liquid, transforming the aerosol into a particle suspension rather than a droplet suspension by the time it reaches CPC 34. A temperature sensor 94 at the end of conditioning zone 92 is operable in conjunction with the heating element to maintain the desired temperature within the conditioning zone. The aerosol is merged with the air flow from conduit 64 through a fitting 96 to provide a diluted aerosol flow of about 3.3 liters per minute to CPC 34. Dilution reduces the dew point to sustain droplet evaporation and reduces the aerosol particle concentration as the aerosol leaves the nebulizer through a fitting 98.
With reference to
A secondary gas may be introduced into nebulizer 30 at a location upstream of the nebulization region as indicated at 99 (
As the particles proceed upwardly through growth region 114, two counteracting phenomena are at work. First, due to the elevated temperature the wetted wick generates increased water vapor, which travels radially inward away from the wick toward the center of passage 108. This of course promotes condensation onto the particles. Second, as the aerosol is heated, the higher temperature tends to discourage condensation. However, because of the relatively high mass diffusivity of water vapor, the water vapor reaches the center of passage 108 more quickly than the heat. Consequently the particles and their immediately adjacent air, even while being warmed, remain sufficiently cool for supersaturation and the resulting condensation and droplet growth.
A laser diode 116 and photodetector 118 are disposed above droplet growth column 102 proximate the aerosol stream. Each droplet alters or interrupts light transmission to the photodetector to generate an analog electrical pulse. The pulses are digitized and provided to processor 38, and the pulse count yields the non-volatile residue concentration.
With reference to
As seen in
As noted previously, the use of water as the condensing fluid avoids health and environmental concerns associated with butyl alcohol and other perflourinated hydrocarbons in CPC 34.
A feature of CPC 34 is that when the particulate concentration increases, the sensitivity is reduced. One factor contributing to this result is that as more particles within a given volume serve as nucleation sites, the heat generated by condensation lowers the supersaturation ratio. This in turn raises the threshold (minimum particle size) for particle nucleation, improving the overall dynamic range of the detector. Another, more prominent factor is the increase in coincidence events with increased concentration. As each droplet intersects the coherent energy beam from diode 116 to generate the corresponding pulse, it also creates a time interval during which any other droplet also intersecting the beam is prevented from generating a pulse, and thus goes undetected.
With reference to
The digital pulses produced by amplifier 132 are provided to a resistance capacitance network having a resistance R and a capacitor having a capacitance C. The capacitor is charged during each digital pulse, i.e. whenever the output of amplifier 132 is at the high level. The RC network generates an output VDT which increases with the charge to the capacitor. Accordingly, voltage VDT represents the total discriminator time for a given sampling interval. Concentration is calculated every 0.10 seconds.
The time constant for the RC circuit is preferably about equal to the signal sampling time, and considerably greater (by orders of magnitude) than the expected widths of the digital pulses.
There is a tendency of VDT to underestimate the actual dead time, and the tendency becomes stronger as particle or droplet densities increase. In accordance with the present invention, system 16 is tested with challenges of known particle sizes and concentrations to determine the relationship between particle concentration and network output VDT to determine a correction function or constant. The resulting constant corrects VDT to particle or droplet concentrations, and is stored to microprocessor 38. Then, in conjunction with providing network output VDT to the microprocessor, the stored function is applied to the voltage to determine particle concentrations. In general, the function is used to determine concentration based on a numerical particle count divided by a product of an adjusted sampling time and the flow rate, which is proportional to the concentration of non-volatile analyte exiting HPLC column 26. The adjusted sampling time is determined by subtracting the discriminator time from the actual sampling time. Thus, a correction factor is applied to the numerical count to yield a higher concentration than the count otherwise would indicate, taking into account the factors noted above.
In one preferred version of the HPLC system, the condensation particle counter can be tuned to exhibit a desired threshold size for droplet growth and a desired droplet growth rate.
Controller 148 is used to adjust a saturation region temperature TS and a growth region temperature TG with respect to each other, as well as individually. An increase in the difference between temperatures TG and TS lowers the nucleation threshold, and thus increases the number of particles counted by the CPC for any given aerosol exhibiting a range of particle sizes. In addition, the rate of droplet growth can be increased by raising both temperatures TG and TS by a given amount, retaining the difference between these temperatures. This adjustment, likewise, tends to increase the particle count resulting from a given aerosol sample.
In accordance with another aspect of the invention, the HPLC system includes a condensation particle counter equipped to use a variety of different working or condensing liquids, for example both water and butyl alcohol. Effective use of both of these fluids requires a reversal in the saturation region temperature TS and growth region temperature TG.
To this end,
As noted above, the mass diffusivity of water exceeds the thermal diffusivity of air. As a result, particles traveling through droplet growth region 154 are being warmed, yet can serve as droplet growth sites because they remain sufficiently cool to condense the surrounding water vapor.
In contrast, the vapor of butyl alcohol has a mass diffusivity lower than the thermal diffusivity of air. In this case, the saturating temperature TS is set higher than the droplet growth region temperature TG. In this arrangement, although the tendency of the wick to generate vapor is reduced along the droplet growth region, this is overcome by the reduced temperature of the particles, which increases their capacity to serve as condensation sites.
According to several alternative liquid chromatography systems, the dried aerosol is selectively modified to remove smaller more volatile components. For example,
The number of diffusion screens 168 can be changed to selectively alter the size distribution of the aerosol particles leaving filter assembly 162. In particular, increasing the number of screens captures and removes a larger proportion of the aerosol particles from the aerosol stream. As a result of this selective filtration, CPC 166 produces an increased signal response for volatile components.
An ion trap 186, disposed along conduit 184, includes an electrically grounded conductive cylindrical wall 188 and a conductive rod 190 electrically isolated from the wall. Rod 190 is negatively biased to a voltage −V to create an electrical field between the rod and the surrounding wall.
As the aerosol passes through ion trap 186, the electrical field causes the ions and the smaller particles, i.e. the higher electrical mobility components, to precipitate onto wall 188. The larger particles tend to continue flowing downstream toward CPC 174.
The ion trap voltage −V can be adjusted to selectively increase or decrease the maximum diameter of particles removed from the aerosol by the ion trap. Also, it is to be understood that various modifications can be employed to yield the same result e.g. reversing the polarities of rod 190 and corona discharge needle 182, biasing wall 188 in addition to or in lieu of rod 190, etc.
Charging device 194 may employ a radioactive charger, or oppositely charged unipolar elements such as corona discharge needles. In either event, aerosol entering DMA 196 has a uniform charge distribution. In a further alternative approach, a unipolar charger is used in lieu of device 194.
The DMA guides the aerosol along a path between a cylindrical outer wall and an electrically charged rod centered and coaxial with the wall. Ions and charged particles with polarities opposite to that of the rod are attracted toward to rod. Higher mobility components precipitate along an upstream region of the rod. Particles with low electrical mobilities precipitate along a downstream region of the rod. Components having electrical mobilities within a selected range between “high” and “low” travel through a slot in the rod between the upstream and downstream regions. The portion of the aerosol containing these midrange components is provided to CPC 198. Thus, in addition to removing small particles, this approach entails removing larger particles as well, to confine the analysis to a particular desired range of particle sizes.
In a departure from the previous nebulizers, conduit 210 is formed by a cylindrical wall 212 that is permeable to the test liquid and adapted to transfer the test liquid vapor to the ambient environment surrounding nebulizer 200 by a process known as perevaporation. To enhance the process, it is desirable to maintain a low relative humidity environment about the nebulizer, although transfer of the sample liquid vapor continues so long as the environment is less humid than the aerosol inside conduit 210.
While not illustrated in
By allowing the test liquid paper to permeate through wall 212 to the ambient environment, conduit 210 tends to lower the dew point of the aerosol. This promotes evaporation without the need to raise the aerosol temperature. The ability to dry the aerosol without heating it considerably enhances the capacity of the system to measure more volatile analytes.
Upstream of optical particle counter 218 is a merger region fluid coupled to conduits 214 and 220 for combing the aerosol and the saturated gas. Due to its lower temperature as compared to the saturated gas, the aerosol upon merger tends to cool the gas, leading to supersaturation and condensation of the working medium onto the aerosol particles. This leads to the growth of droplets, which are optically sensed as before.
Downstream, a laser diode 232 generates a laser beam 234 that intersects the aerosol stream. Light scattered by droplets 230 is received by a photodetector 236 configured to sense droplets 230 individually, providing a signal via a line 238 to a processor 240 each time one of the droplets traverses a viewing volume determined by the intersection of laser beam 234 and the aerosol path. Photodetector 236 further is configured to sense multiple droplets simultaneously by generating an electrical signal having an amplitude proportional to the amplitude of light scattered in concert by multiple particles. This signal is provided to the processor via a line 242.
Photodetector 236 provides for high accuracy at low analyte concentrations, based on the droplet count over a given sampling time. When an analyte concentration becomes too high for individual counting, processor 240 is configured to use the active analyte concentration input from line 240, i.e. the photometric measurement.
Thus, in accordance with the present invention, a system for monitoring analyte concentrations in water and other liquids generates more reliable information virtually in real time, to facilitate more effective management of processes that depend on analyte identification and measurement. The system can be tuned to adjust nucleation thresholds and droplet growth rates, and accounts for coincidence episodes and thermal depletion to extend the useful range for generation of concentration data based on particle counts.
This application claims the benefit of priority based on Provisional Patent Application No. 60/857,609, entitled “System for Separating Non-volatile Analytes and Measuring Analyte Concentrations,” filed Nov. 7, 2006.
Number | Date | Country | |
---|---|---|---|
60857609 | Nov 2006 | US |