Patent Application
20100242632
The separation and collection of particulates/aerosols from an air stream (or other fluid stream) is of concern in several contexts. In some cases, the goal may be to simply remove the particulates/aerosols from the fluid stream, thereby cleaning or purifying the fluid. Often it is desired to remove all particulates, regardless of composition, if the particulates are above a certain size. For example, automobile painting and the fabrication of silicon chips in clean rooms represent two situations in which all particulates large enough to result in an inferior product are desirably removed from the processing environment.
In other cases, particulates are collected for analysis to determine the type and concentration of such particulates/aerosols entrained in the fluid. For example, this technology may be employed in the detection of airborne biological or chemical warfare agents, the detection of biological contamination in confined spaces, such as aircraft or hospitals, or the detection of industrial pollutants (either in ambient fluid or in the effluent of smokestacks).
Much effort has been expended in the past in the detection and classification of particulates or aerosols in fluid streams. Various technologies have been employed to remove particles from an air stream to obtain a sample for analysis, including cyclones, impactors, and filters. Impactors generally direct a stream of fluid containing the particulates toward an impactor plate. Due to their inertia, the particulates striking the impactor plate are collected on its surface, while the fluid is deflected to the side. One potential problem with such impactors is that particulates may bounce off the impactor's collection surface upon impact and thus avoid collection. It would be desirable to provide improved impactors that minimize such an undesirable characteristic.
Virtual impactors have been used to sort particulates entrained in a flow of fluid based on particle size, as well as to increase the concentration of particles of a desired size. When used in connection with an impactor, greater control over the particles deposited on the impaction surface can be achieved. Virtual impactors may operate on a number of different principles, but all avoid actual “impact” as a means to separate particulates from a fluid in which the particulates are entrained, and rely on differences in particulate mass to induce inertial separation. Specifically, a particulate-laden fluid stream is directed toward a surface presenting an obstruction to the forward movement of the fluid stream. The surface preferably includes a void at the point where the particulates would normally impact the surface, to minimize actual impaction. When a major portion of the fluid stream changes direction to avoid the obstruction presented by the surface, fine particulates remain entrained in the deflected major portion of the fluid stream. Heavier or denser particulates, on the other hand, fail to change direction and remain in a minor portion of the fluid. The threshold particulate size that generally determines whether a particle will be entrained in the minor flow or the major flow is referred to as the cut size. For example, a virtual impactor having a cut size of 10μ will separate a flow of fluid into a major flow containing the majority of the fluid and the majority of particles smaller in size than 10μ, and a minor flow that includes a minor portion of the fluid, and a majority of the particles over 10μ. The concentration of particles over 10μ in the minor flow is thus substantially increased (due to the reduction in volume of the fluid in the minor flow). Concentration increases of about 10-fold are readily achievable, and virtual impactors in series can readily achieve concentration increases of about 100-fold. Some examples of virtual impactors can be found in U.S. Pat. Nos. 3,901,798; 4,670,135; 4,767,524; 5,425,802; and 5,533,406.
Once particulates have been collected (for example, deposited on an impaction surface), the particles can be analyzed to characterize the particles (i.e., biological or not, for example, using relatively simple optical techniques) or to more specifically identify the particles (which may require application of more sophisticated analytical techniques). The specific analytical technique employed will dictate whether the particles on the collection surface can be analyzed in place, or whether a liquid or gaseous sample needs to be obtained before analysis.
Accordingly, a need exists to develop a method and apparatus capable of providing samples collected from a fluid stream with minimal operator effort, and minimal chance of contamination. Such samples desirably should include a high concentration of particulates of a desired size. It would further be desirable to provide method and apparatus for removing collected particulates from an impact collection surface, and to transfer such particulates in a liquid or gaseous state to an appropriate analytical component for analysis. To facilitate adoption of such technology, it would be desirable for such apparatus to exhibit minimal operational costs and require minimal operator involvement once the apparatus has been properly configured.
Overview of the Concepts Presented Herein: The concepts disclosed herein are directed to a number of exemplary methods and apparatus for removing particles/particulates from a fluid stream and depositing such particles/particulates on one or more collection surfaces. Preferably, a concentrator is employed to increase a concentration of particles larger than a first predefined particle size in at least a portion of the fluid, thereby achieving a concentrated volume of fluid. While it should be recognized that the concepts disclosed herein can be applied to removing particles from many different kinds of fluids, a particularly useful application is removing particles from air. However, where the following description specifically uses the term “air,” it should be recognized that the concepts being discussed can also be applied to other fluids. Thus, the concepts being disclosed are generally not intended to be limited to removing and/or collecting particles and particulates from air alone. The concentrated volume of fluid is then directed to the collection surface(s), such that particles in the concentrated volume of fluid are deposited upon the collection surface(s). Preferably, the concentrator is implemented using a virtual impactor. Such a virtual impactor generates a minor flow including a minor portion of the concentrated volume of air and a major portion of particles larger in size than the first predefined particle size, and a major flow including a major portion of the concentrated volume of air and a minor portion of particles larger in size than the first predefined particle size. The minor flow is directed to the collection surface(s) for removal of the particles.
In some exemplary embodiments, the collection surface comprises a plurality of beads, where the beads are substantially larger than the particles in the fluid stream. The fluid stream containing the particles is passed through a bed of beads. The particles are removed from the fluid stream as the particles impact various beads as the fluid stream traverses the bed of beads. Significantly, the bead bed substantially enhances collection efficiency, because if a particle just misses or bounces off one bead, it will likely encounter additional beads upon which it may impact and adhere. If a single impaction surface is employed, it is possible that particles bouncing off the single impaction surface will not be collected.
In some exemplary embodiments, a pre-filter is used to remove particles larger than a second predefined particle size. For example, a pre-filter removing particles larger than about 10μ can be employed (because many particles of interest may be smaller than 10μ in size). The pre-filter can be implemented using a filter comprising a plurality of pores smaller in size than the second predetermined particle size, an impactor, or a virtual impactor. When a virtual impactor is employed, the major flow, comprising the majority of the volume of fluid and a majority of particles smaller in size than the second predefined particle size is conveyed to the concentrator.
In some exemplary embodiments, a sample preparation component is configured to generate at least one of a gaseous sample and a liquid sample including particles removed from the concentrated volume by the collection surface(s). In some cases, the sample is generated without requiring removal of the collection surface(s) from the apparatus. To generate a gaseous sample, a heater or laser can be used to vaporize particles deposited upon the collection surface. To generate a liquid sample, a rinse liquid can be used to wash particles from the collection surface. In some exemplary embodiments, an analytical component is included to analyze the sample generated by the sample preparation component. In some embodiments, the sample is thus analyzed without requiring removal of the sample from the apparatus.
In some exemplary embodiments, the collection surface includes a coating configured to enhance collection of particles from the concentrated fluid stream. The coating can comprise a material characterized by its ability to retain particles impacted thereon when dry, and having a relatively low coefficient of adhesion when wet, so that the particles that have impacted on the collection surface and been retained thereon are readily washed from the surface with a liquid. The coating can comprise a material that attracts substantially only biological particles of a specified type, for efficiently separating said particles from the concentrated volume of fluid, the coating binding with the particles of the specified type to retain them on the collection surface. The coating can comprise a material that changes state while being retained on the collection surface, a first state of the material characterized by its ability to retain the particles that impacted thereon, separating the particles from the concentrated volume of fluid, and a second state of the material being characterized by its ability to readily release the particles separated from the concentrated volume of fluid.
It should be recognized that other aspects of this technology also encompass exemplary methods incorporating steps substantially similar to the functions implemented by the elements discussed above.
This Summary has been provided to introduce a few concepts in a simplified form that are further described in detail below in the Description. However, this Summary is not intended to identify key or essential features of the claimed subject matter, nor is it intended to be used as an aid in determining the scope of the claimed subject matter.
Various aspects and attendant advantages of one or more exemplary embodiments and modifications thereto will become more readily appreciated as the same becomes better understood by reference to the following detailed description, when taken in conjunction with the accompanying drawings, wherein:
Exemplary embodiments are illustrated in referenced Figures of the drawings. It is intended that the embodiments and Figures disclosed herein are to be considered illustrative rather than restrictive. No limitation on the scope of the technology and of the claims that follow is to be imputed to the examples shown in the drawings and discussed herein.
In the following description, the prefix “micro” is applied generally to components that have sub-millimeter-sized features. Micro-components are fabricated using micro-machining techniques known in the art, such as micro-milling, photolithography, deep ultraviolet (or x-ray) lithography, electro-deposition, electro-discharge machining (EDM), laser ablation, and reactive or non-reactive ion etching. It should be noted that micro-machined virtual impactors provide for increased collection efficiency and reduced pressure drops.
Also as used hereinafter, the following terms shall have the definitions set forth below:
Particulate & particle—any separately identifiable solid, semi-solid, liquid, aerosol, or other component entrained in a fluid stream that has a greater mass than the fluid forming the fluid stream, and which is subject to separation from the fluid stream and collection for analysis. It is contemplated that the particulates & particles may arise from sampling almost any source, including but not limited to, air, water, soil, and surfaces, and may include inorganic or organic chemicals, or living materials, e.g., bacteria, cells, or spores.
Fluid—any fluid susceptible to fluid flow, which may comprise liquids or gases, and which may entrain foreign particulates & particles in a flow thereof. Unless otherwise noted, “fluid” shall refer to an ambient or source fluid containing un-concentrated particulates that are subject to collection, not a fluid into which the particulates are concentrated after collection or capture.
Spot—an aggregate of particulates or particles deposited upon a collection surface in a relatively small area, so that the individually small particulates are aggregated together to form a collection of such particles larger than a single such particle, which can be more readily observed by magnification or by the naked eye.
The following description first describes an embodiment for an exemplary particle sampler in terms of its basic functional elements. Then, each functional element is discussed in greater detail, and finally, additional exemplary embodiments are discussed.
Housing 12, while not strictly required, is preferably implemented to protect the additional functional elements discussed below, and to facilitate transportation of the air sampler. Those of ordinary skill in the art will readily recognize that air samplers of many different form factors and sizes can be implemented consistent with sampler 10. Relatively larger air samplers capable of sampling relatively larger volumes (or volumetric flows) of air may be implemented in buildings, whereas relatively smaller air samplers can be made to be portable, so as to be readily moved from one location to the next to sample air (or other fluid) in a plurality of different locations.
Pre-filter 14 is a device that performs one or more of the following functions: (a) removes over-sized particles that are too large to be of interest (for example, those greater than 10 microns in diameter), (b) rejects or removes rain, snow, and other water precipitation, (c) restricts insects from crawling or flying into the apparatus, and (d) rejects or removes other flying debris. Rejecting oversized particles may be a desired functionality for some applications. As discussed in greater detail below, pre-filters can be implemented using inertial impactors configured to remove such oversized particles (the term oversize indicating that the particles are larger than a particle size that is of particular interest), virtual impactors, or filters including a plurality of pores smaller in size than the oversized particles.
Concentrator 16 is configured to discard a portion of the air introduced into the concentrator without also discarding a majority of the particles of interest, thereby increasing the concentration of particles of interest in the remaining portion of the air (i.e., that portion of the air that has not been discarded) to enhance collection efficiency. Virtual impactors represent a particularly preferred technology used to implement such concentrators. A virtual impactor is a device that will separate a fluid flow (such as air) into a minor flow (i.e., a smaller fraction of the fluid flow) containing a majority of particles larger than a cut size, and a major flow (i.e., a major fraction of the fluid flow) containing particles smaller than the cut size. Virtual impactors are available that exhibit relatively low pressure drops (which may be desirable because relatively low pressure drops minimize power requirements) across each stage and that can be injection molded at a relatively low cost. When an impactor surface is introduced into the minor flow, a relatively high collection efficiency can be obtained. Depending upon a nozzle size associated with the outlet of the minor flow, a spot size of less than 3 mm can be generated on the collection surface. Such small size has the advantage of concentrating the collected particles in a relatively small area, which simplifies subsequent removal of such particles to obtain a sample. The virtual impactor provides initial particle concentration by separating particles of interest from the bulk of the fluid flow. For example, particles ranging from about 1 to about 10μ in size can be concentrated, and the volumetric flow of air significantly reduced. Multiple virtual impactors can be arranged in series to achieve higher particle concentrations.
Particle collector 18 is configured to collect particles of interest from the remaining portion of air (i.e., that portion of the air that has not been discarded by the concentrator). In general, particle collector 18 includes one or more collection services that remove particles from the air by impaction (i.e., the particles entrained in the air collide with the collection surface and are retained thereon). The concepts disclosed herein encompass several different types of collection surfaces. As discussed in greater detail below, collection surfaces can be treated with specialized coatings to enhance collection efficiency.
Sampling component 20 is configured to obtain a sample from the particles deposited upon the collection surface, and to prepare the particles for analysis by an analytical component. The type of sample obtained and the sample preparation required will vary depending on the specific analytical component employed. For example, some analytical components require dry samples, some require wet samples (i.e., samples contained in a volume of liquid), and still other types of analytical components require gaseous or vaporous samples. Gaseous and vaporous samples can be obtained by desorbing a sample from a surface using heat (which can be supplied by various elements, such as an infrared lamp, an electrical resistive heater, or a laser). Gaseous/vaporous samples can also be obtained by dissolving the sample in a solvent and flash vaporizing the solvent. Since the use of relatively large volumes of solvents/reagents in field samplers is undesirable, because providing the solvents/reagents presents an additional logistics problem, it may be desirable to employ an air sampler that uses minimal volumes of such solvents/reagents.
In at least some embodiments sampling component 20 can regenerate the collection surface in the process of obtaining the required sample. The term “regenerating the collection surface” should be understood to mean removing the collected/deposited particulates, such that previously collected particulates will not contaminate future samples. Such regeneration can be achieved in a plurality of different ways, some of which are discussed in detail below. Where a liquid sample is obtained, rinsing the collection surface may simultaneously obtain the sample and regenerate the collection surface. Where a vaporous sample is obtained, heating the particulates/collection surface may simultaneously obtain the sample and regenerate the collection surface. In other embodiments, relative motion between particle collector 18 (i.e., the collection surface) and the minor flow outlet of concentrator 16 enables particles to be deposited on different portions of the collection surface over time, such that previously deposited particles do not contaminate subsequent samples. In such an embodiment, regeneration of the collection surface is not required (although such functionality may be implemented if desired). The relative motion can be achieved by coupling a prime mover to at least one of the minor flow outlet (or the outlet of a conduit through which the minor flow is directed) and the collection surface.
In some embodiments, a portion of the collection surface may be removed to obtain a sample, and another portion of the collection surface is placed in fluid communication with the concentrator to collect additional particles to be used to obtain a future sample. In still other embodiments, a mechanism is included to clean the collection surface after a sample has been collected. Such cleaning mechanisms include, but are not limited to, liquids, compressed air, cleaning pads, and cleaning brushes.
As noted above, analytical component 22 can be implemented using various types of analytical instruments, including but not limited to: fluorescence-based sensors; chemical sensors; particle counters; spectrophotometers; gas chromatographs (GC); mass spectrographs (MS); and combinations thereof (for example, a GC/MS). Clearly, the sampling component implemented is based on the analytical component that will be employed.
Not specifically shown in
Several factors, beyond the type of analytical component that will be used to analyze the sample obtained by air sampler 10, can affect the specific implementation employed. For example, the flow rate of the sampler is dependent upon the power requirement and size requirement of the sampler. Thus, air samplers intended to have higher flow rates will generally be larger and require more power. For portable air samplers, small size and small power requirements (hence relatively low flow rates) are generally preferred; however, greater performance can be achieved using larger sizes and more power. Higher flow rates generally correspond to higher sensitivities. For portable units, battery-based power supplies will represent a significant percentage of the weight of the sampler.
In determining a design for a sampler, each of the following can represent an important consideration: environmental compatibility, sensor system compatibility, concentration factor, particle size selectivity, reliability, logistics (size, weight, power, and noise), operating cost, and initial cost. Different end-users having different applications in mind will weigh these factors accordingly, based on their requirements. Some trade-off between these parameters might be employed to customize a sampler design to the specific requirements of a user.
With respect to sensor system compatibility, a critical question to be answered is for what purpose will the sampler be used? Some exemplary uses include: initial warning or screening of air samples for bio or chemical hazards in the field; chemical identification of samples in the field; chemical confirmation of samples in the lab; and forensics investigations.
With respect to environmental compatibility, relevant factors associated with outdoor environments include operating humidity, temperature, susceptibility to wind, rain, and the presence of pollutants in the environment (such as engine exhaust and other pollutants in an urban environment). Relevant factors associated with indoor environments can include: low humidity (often associated with mail rooms), a high loading of paper dust (also often associated with mail rooms), and a high loading of other particulate contaminants (often associated with battlefields and subways).
Concentration factor is a measure of the effectiveness of the sampler to concentrate aerosols for a specific application. Low vapor pressure chemicals may be present in an aerosol form, or may be impregnated into or condensed onto a carrier aerosol.
Particle size range is another factor; respirable particles (i.e., particles that may be of particular interest because their relatively small size allows them to be inhaled) are generally considered to be particles ranging in size from about 1 g to about 10 g. Chemicals in the air may be in the form of submicron particulates or vapors. Low vapor pressure chemicals may pose a threat over a much broader range (e.g., from about 0.01μ-100μ). The size of the particles of interest (i.e., those particles the air sampler is specifically configured to collect) will affect the design of the pre-filter, the concentrator, and the particle collector, because such elements can be specifically configured to enhance collection of particles of a predefined size (or size range).
In one exemplary embodiment, preferred (but not limiting) design parameters for sampler 10, which is intended to output a liquid sample, include continuous autonomous operation, relatively high flow rate (up to 800 L per minute, with a particularly preferred range being about 300-400 L per minute), a system collection efficiency of approximately 60%, the ability to output a liquid sample (using automated sample extraction) in 0.5 to 1 mL buffer solutions (minimizing the consumption of reagents), and the ability to direct the liquid sample into an integrated third-party detection system. For some embodiments, preferred (but not limiting) design parameters for sampler 10 that is intended to output a vapor or gaseous sample include continuous autonomous operation, relatively high flow rate (up to 800 L per minute, for example, with range of about 300-400 L per minute), a system collection efficiency of approximately 60%, the ability to output a gaseous sample (using automated sample extraction), and the ability to direct the gaseous sample into an integrated third-party detection system. An optimal strategy for low vapor pressure chemical sampling will likely combine traditional vapor sampling with advanced aerosol sampling. It may also be desirable to combine low pressure drop virtual impactors with an impactor to concentrate aerosol particles into a very small area, which offers the highest potential concentration factor, and a relatively low operating cost. As discussed below, if desired, a regenerable surface technology can be implemented to enhance the operational life of the sampler.
In one embodiment, schematically illustrated in
Note that virtual impactor 28 is configured to discharge minor flow 30 from the sampler via outlet 34. Those of ordinary skill in the art will readily recognized that while the pressure drop through a virtual impactor is highest at the minor flow outlet as compared to the major flow outlet, both the minor flow outlet and the major flow outlet can be coupled in fluid communication with a low-pressure source (such as a fan or pump) to draw fluid through the virtual impactor. For example, fan 32 is disposed between minor flow 30 and outlet 34, to draw air from inlet 26 through virtual impactor 28. As described in greater detail below, major flow 36 is coupled in fluid communication with other fans. While the fan could be disposed upstream of the virtual impactor to force air through the virtual impactor (providing high pressure at the inlet of the virtual impactor, such that ambient pressure corresponds to the low-pressure source), such a design is less preferred, because it increases the turbulence in the air flow and interferes with particle collection. Minor flow 30 includes a minor portion of the air that entered virtual impactor 28, and a majority of the particles larger than a cut size associated with the virtual impactor. Thus, virtual impactor 28 is acting as a filter that discards the majority of the particles larger than the cut size. Where the air sampler is designed to sample respirable particles, a particularly preferred cut size is about 10μ (although it should be recognized that such a cut size is intended to be exemplary, rather than limiting). Major flow 36 exiting virtual impactor 28 includes a majority of the air that entered virtual impactor 28, a minority of the particles larger than the cut size, and a majority of the particles smaller than the cut size. Thus, careful selection of the cut size associated with virtual impactor 28 insures most of the particles of interest are entrained within major flow 36. Note that very little concentration of the particles of interest has yet been achieved, as relatively little air has been discarded through the minor flow.
Virtual impactor 38 (which is acting as the concentrator) is disposed downstream of virtual impactor 28 (which is acting as the pre-filter), such that major flow 36 is directed into virtual impactor 38. Once again, both a major flow 40 and a minor flow 44 exit virtual impactor 38. Major flow 40 includes the majority of the air entering virtual impactor 38, and a minority of the particles larger than the cut size associated with virtual impactor 38. Major flow 40 is directed to outlet 34 via a fan 42 disposed between virtual impactor 38 and outlet 34. Those of ordinary skill in the art will readily recognize that in some embodiments a single fan can be used to implement fans 32 and 42, and it should be recognized that the present disclosure encompasses such an embodiment. The use of a plurality of fans can provide a benefit in that achieving a desired pressure balance through the air sampler can be easier if a plurality of fans are implemented. Minor flow 44 exiting virtual impactor 38 includes a minor portion of the air that entered virtual impactor 38, as well as a majority of the particles greater than the cut size associated with virtual impactor 38, thereby achieving concentration of the particles of interest by discarding a majority of the air and a majority of particles smaller than the cut size.
Collection surface 46 (implementing the particle collector of
As discussed above in detail, sampling component 20 is configured to obtain a sample from the particles deposited upon the collection surface, and to prepare the particles for analysis by analytical component 22. The specific analytical component will determine the type of sample (i.e., dry, wet, vaporous, or gaseous) provided by sampling component 20. It should be recognized that some analysis components may not require removal of particulates from the collection surface. For example, optical detection of biological particles by stimulating their fluorescence can be achieved without removing biological particles from a collection surface. Thus, it should be recognized that the concepts disclosed herein encompass embodiments where sampling component 20 is not required. Where sampling component 20 is not required, a regeneration component may be used to clean the collection surface to facilitate collection of additional particles for subsequent analysis, without fear of contamination by the presence of previously collected particles.
Having discussed several exemplary embodiments of air samplers in accord with the concepts disclosed herein, details relating to the three different types of pre-filters that can be beneficially employed in such air samplers will now be provided. As noted above, inertial impactors, filters including a plurality of pores, and virtual impactors can be used as pre-filters.
As a result of inertia, most of the particulates that are greater than the selected cut size are conveyed in this small minor flow and exit the virtual impactor. Most of the particulates smaller than the virtual impactor cut size are exhausted with the majority of the inlet air as the major flow. The stopping distance of a particle is an important parameter in a virtual impactor design. The cut point (size at which about 50% of the particles impact a surface, i.e., flow into the second nozzle) is related to the stopping distance. A 3 micron particle has nine times the stopping distance of a 1 micron particle of similar density.
In an exemplary, but not limiting embodiment, the air velocity through an inertial impactor is greater than about 10 m/s and less than about 100 m/s, and may be greater than about 20 m/s and less than about 30 m/s. The nozzle diameter is greater than about 0.25 mm and less than about 2.5 mm, and can be greater than about 0.5 mm and less than about 1 mm. The nozzle is located at a distance from the impaction surface greater than about 0.1 mm and less than about 2 mm, and can be at a distance greater than about 0.25 mm and less than about 0.5 mm.
In an exemplary, but not limiting embodiment, the inertial impactor is configured for optimum collection of particles in about the 0.5-10 μm diameter, and can be in the about 1 μm-5 μm range. Airborne particles in this range are the most likely to represent an inhalation hazards to humans. Within this range, bacteria would be captured, as well as potentially noxious viruses or protein aggregates. However, the inertial impactor may be configured for optimal collection of particles of other size ranges, in different applications.
A sample of particles deposited in the bead bed can be removed by rinsing the bead bed with a solvent. Agitating the bead bed may facilitate sample extraction. The agitation can be implemented using ultrasonic or sonic waves, or by otherwise physically moving the bead bed. Depending on the type of particulates that have been collected, heating the bead bed may be used to obtain a gaseous or vaporous sample. Once a sample has been collected, the bead bed can be regenerated and prepared to collect additional particles by rinsing the bead bed with an aqueous solution, preferably including a surfactant. Empirical studies have shown that aqueous solutions including about 0.5% surfactants can be beneficially employed to regenerate a bead bed. The beads themselves can be implemented by generally spherical (or granular) polymer or glass beads. Inorganic substrates may also be used as well. In general the beads will be inert, although it should be recognized that any of the coatings discussed below with respect to enhancing collection efficiency can be beneficially incorporated onto one or more of the beads. In some embodiments, only some of beads in the bead bed include a coating, while in other embodiments, substantially all of the beads in the bead bed include a coating. In still other embodiments, some of the plurality of beads have been coated with a first material, while other beads have been coated with a different material. Coating different beads with different materials will facilitate collection of disparate particles, which under some circumstances, may not be desired, but which may be desirable in other sampling paradigms. In general, deeper bead beds will have better collection efficiencies. In at least one embodiment, the bead bed is about 50 beads deep, although this bead depth is intended to be exemplary, rather than limiting.
For the air samplers described herein, several types of virtual impactor and impactor combinations are suitable for use in collecting samples of particles as spots on a substrate. As noted above, concentrating particles deposited on an impaction surface as the spot facilitates subsequent collection of a sample. Because the specific design of the inertial impactor (including a nozzle directing the airflow towards the impaction surface) can be optimized for a particular size of particles, it is contemplated that at least some embodiments disclosed herein may include multiple nozzles, each with a different geometry, so that multiple particle types can be efficiently collected.
In an exemplary embodiment, the nozzle directing the gaseous fluid toward the impaction plate/sample substrate is a spotting nozzle. The spotting nozzle receives a gaseous fluid from an inlet, accelerates the gaseous fluid within the nozzle body, and discharges the accelerated fluid through an outlet. The spotting nozzle thus directs a jet of accelerated gaseous fluid toward the impaction plate. The spotting nozzle increases the mean velocity of the gaseous fluid to provide sufficient momentum to particles above a specific size so that such particles are able to impact and be retained upon the impaction plate/sample substrate. For example, a gaseous fluid sample may be sucked through a nozzle having a reduced cross-sectional area relative to a source of gas using a downstream vacuum pump. The spotting nozzle is preferably configured to deposit a spot of particles onto the impaction plate/sample substrate. The term “spot” as used herein is intended to represent an aggregate of particulates or particles deposited upon a substrate in a relatively small area, such that the spot region has relatively high numbers of particles on the substrate in the spot area and the area outside the spot includes substantially fewer particles (or none) on the substrate, i.e., a spot, a relatively dense group of particles which can be more readily observed by magnification, with the unaided eye, or using other detection techniques.
Preferably, the intake of the spotting nozzle is downstream of a virtual impactor, such that the gaseous fluid accelerated by the spotting nozzle is concentrated with respect to the particles entrained within the gaseous fluid. The term “downstream” is intended to indicate that the spotting nozzle and the virtual impactor are configured so that the gaseous fluid passes first through the virtual impactor, and then through the spotting nozzle. As discussed above, a virtual impactor is an apparatus that increases the concentration of airborne particles of a desirable size range. It separates an airflow into a minor and a major component, wherein the minor component carries a majority of airborne particles above a certain size. Examples of virtual impactors can be found in U.S. patent application Ser. No. 09/955,481, or in U.S. Pat. Nos. 3,901,798; 4,670,135; 4,767,524; 5,425,802; and 5,533,406. Thus, the spotting nozzle can be downstream of the minor flow of a virtual impactor. The virtual impactor can increase the concentration of particles that are above about 1 μm in size. In some embodiments, more than one virtual impactor can be placed upstream of the spotting nozzle. Impacting air with higher concentration of airborne particles in the desired range increases the collection pace and thus, the efficiency or sensitivity of this novel device. It should be recognized at the spotting nozzle in the outlet of the virtual impactor may be separated by some distance. Flexible tubing, hose, or some other type of conduit can be used to couple the outlet of the virtual impactor to the spotting nozzle. Preferably, the spotting nozzle is disposed adjacent to the collection surface.
In one preferred embodiment, two virtual impactors are connected in series, such that a concentration of particulates entrained in the minor flow of gaseous fluid exiting the second virtual impactor is approximately 70 times the original concentration.
As shown in
Note that in
It should be noted that the collection surface, with or without a coating, need not be flat. For example, a surface with portions raised significantly above the bulk of the surface can also be used to collect spots of particulates. Thus, a textured surface with portions raised substantially above a background portion of the surface can be used to collect spots of particulates. Such textured surfaces are disclosed in commonly assigned U.S. Pat. No. 6,110,247, the disclosure and drawings of which are hereby specifically incorporated herein by reference. Such surfaces reduce the tendency of particles to bounce and therefore increase spot formation efficiency.
Surface Coatings for Collection/Impaction Surfaces: FIGS. 5 and 6A-6C schematically illustrate how coating an impact collection surface, with a material can substantially enhance the efficiency of that surface.
The relatively greater density of particulates 414 evident on coated impact collection surface 416, compared to impact collection surface 412, is due to a characteristic of the coating that causes it to better retain particulates and thus more efficiently separate the particulates from the fluid in which they are entrained, compared to the prior art impact collection surface that is not coated. In the embodiment shown in
In an alternative exemplary embodiment shown in
The material used for producing coated impact collection surface 423 and other coated areas or surfaces employed in this description for collecting particulates in accord with the concepts disclosed herein, is selected based upon certain characteristics of the material that increase the efficiency with which the particulates are separated from the fluid in which they are entrained. Each material used for a coating has certain advantages that may make it preferable compared to other materials for separating a specific type of particulate from a specific type of fluid. For example, for use in collecting particulates in dry air or other dry fluid, a material called TETRAGLYME can be used for the coating. This material is hydrophilic until it is exposed to water and when dry, is relatively very sticky, tending to readily retain particulates that impact it. However, once water is sprayed onto the TETRAGLYME coated surface so that it is wetted, the coating becomes hydrophobic. When hydrophobic, the TETRAGLYME coated surface is no longer sticky or tacky, and in fact, readily releases the particulates that previously were retained by it. The water (or other liquid containing water) easily washes the particulates away from the coated impact collection surface. TETRAGLYME, which is available from a number of chemical supply houses, is bis(2-[methoxyethoxy] ethyl)ether tetraethylene glycol dimethyl ether dimethoxy tetraethylene glycol and has the formula: CH3OCH2(CH2OCH2)3CH2OCH3CH3—O—CH2—CH2—O—CH2—CH2—O—CH2—CH2—O—CH2—CH2—O—CH3. Tests have shown that TETRAGLYME coating can collect more than three times as many particulates as an uncoated surface. Water molecules are retained by the molecule by links to the oxygen atoms, as shown below.
A second type of material usable for a coated particulate collection surface is PARYLENE, which is a tetrafluoromore manufactured and sold by DuPont Chemical Company under the trademark INSUL-COTE™, Type N. The PARYLENE material is characterized by a relatively low coefficient of friction, causing it to be extremely slippery and not sticky. Accordingly, particulates impacting against a coated surface comprising PARYLENE are initially separated from the fluid in which they are carried by the impact with the coated surface and are initially retained by the coated surface. However, these particulates are readily washed away from the PARYLENE coated surface by water or other liquid sprayed onto the coating. The particulates retained by a PARYLENE coated surface on tape 420a are readily washed away from the coating by water or other liquid spray.
The TETRAGLYME material is an example of a class of materials that has two distinct states related to particulate collection. When dry and hydrophilic, the TETRAGLYME material is in a first state, in which it is sticky and is very efficient at separating particulates from the fluid in which they are entrained, compared to an uncoated surface. However, when wetted, the TETRAGLYME material changes to its second state, in which it readily releases the particulates.
As shown in
It is also contemplated that the coated impact collection surface need not be planar. Indeed, it is likely that enhanced particulate collection efficiency can be achieved by using a non-planar coated surface to collect particulates.
In at least one embodiment, the collection surface incorporates a material that helps maintain the particulates deposited on the collection surface in good condition, without substantial degradation. For some particles, such as living cells, this material may be a liquid that contains nutrients. Applying a hydrogel or equivalent coating on the collection surface would allow localization of water. The water can be used to deliver salts, sugars, proteins, and other nutrients to enable the cells to survive on the collection surface during the time interval between deposition on the collection surface and subsequent analysis of the collected samples of particulates.
For all of the collection surfaces noted above, some portion of the analysis/detection scheme could be included as part of the surface. For example, if the analysis employed to detect a specific particulate involves incubating the collected particulates (some of which are likely to be bioparticles) with a reagent, the reagent can be incorporated onto the surface so that the incubation period is initiated upon deposition.
Sampling Component: As discussed above, particularly preferred air samplers in accord with the concepts disclosed herein beneficially incorporate a sampling component configured to remove at least a portion of the particles deposited upon the collection surface such that a sample of particles can be conveyed to an analytical component for analysis. The types of particles the air sampler has been designed to collect will play a significant role in determining the type of analytical component that will be used to analyze the particles, and the type of sampling component required to obtain the necessary sample. For example, some analytical components require dry samples, some require liquid samples, and still others require gaseous samples. The specific sampling component implemented will be configured to provide a sample required for a specific analytical component.
With respect to sampling components configured to provide a liquid sample, the sampling component will need to incorporate a liquid rinse supply volume configured to store a volume of liquid to be used to generate a liquid sample. The liquid can be an organic solvent or an aqueous solution (such as saline). The specific liquid employed should be selected based on the analytical component implemented (because some liquids may be incompatible with certain analytical techniques), as well as the type of particle being sampled (and because some liquids may be incompatible with specific types of particles; if the particles are biological in nature, and the analytical technique requires the biological particles be alive, then liquids toxic to the biological particles cannot be employed). A liquid sample can be prepared by rinsing the collection surface with the liquid to remove the particles, using some other mechanism (such as a mechanical scraper or a jet of compressed air) to dislodge particles that are then introduced into the liquid, or by removing a portion of the collection surface and introducing that portion into a volume of the liquid (or some combination thereof). The use of relatively small volumes (i.e., on the order of milliliters or less, although it should be recognized that such a metric is intended to be exemplary, rather than limiting) of liquid to prepare the liquid sample provides several benefits. First, the smaller the volume of liquid, the more concentrated the particles that will be in the sample, generally facilitating the analysis. Second, using relatively small volumes of liquid to generate each sample will reduce the liquid supply that needs to be incorporated into the air sampler, which enables smaller, more compact, and more readily portable air samplers to be achieved.
One exemplary embodiment of an automated system that automatically changes collection surfaces when triggered to do so (or according to a pre-programmed schedule) includes a plurality of tickets. This Indexed Particle Collection System (IPCS) allows multiple samples to be taken without user intervention. Unused collection tickets are stored in a “magazine.” When a new sample is needed, the indexed system automatically removes a new collection ticket from the fresh magazine and places it in position for sample collection. When the sample is complete, the collected sample is moved into a spent magazine and a fresh ticket is placed into position for collection of the next sample. In a prototype unit, up to 24 sample tickets fit in a magazine. Samples can be changed on a pre-programmed time interval or by a trigger signal.
To collect a sample, a ticket is loaded into a collection zone 924 from a fresh magazine 926. Once the sample is collected, the ticked is moved to a spent magazine 928, and a new ticket is placed into the collection zone from fresh magazine 926. While not separately shown, it should be understood that a prime mover is employed to move the tickets from the fresh magazine to the collection zone, and then to the spent magazine. Each impact surface 908 of the tickets can incorporate any of the coatings discussed above, or no coating. Each impact surface on a ticket can be provided with the same coating, particularly if one impact surface will be archived. Of course, in some collection strategies, such as when comparing the collection efficiency of one coating to another, different coatings can be employed. System 915 does not incorporate any rinsing of the sample to produce a liquid sample, but rather is intended for use in applications where the samples would be returned to a laboratory for analysis.
General Rinse System Concept: While system 915 is quite useful for collecting dry samples for later analysis or archiving, many analytical techniques require samples in liquid form. One way to include such functionality would be to provide a rinsing module as a separate, add-on module to a sampling system, as indicated by module 932 in
The basic steps of the rinsing preferably include: (1) receiving a signal to rinse a collected sample; (2) removing the appropriate ticket from either the collection zone or the spent magazine; (3) delivering the appropriate ticket to the rinse module; (4) applying a rinse liquid to the ticket in the rinse module; (5) agitating or otherwise performing steps to facilitate removal of material from the ticket in the rinse module and into the liquid to produce a liquid sample; (6) delivering the liquid sample to a sample vial; and, (7) delivering the required liquid sample volume from the sample vial to the analysis system.
One variation would be to include the step of removing only the portion of the collection surface on the ticket that contains the spot of impacted particles, which will minimize the rinse volume required to remove the particles. Such minimal removal may correspond to a physical removal (or “punching out”) of the impaction spot. Conversely, such minimal removal can be achieved using means (such as a sample tube that is brought in contact with, or immediately adjacent to, the surface of the ticket) that isolates the spot and minimizes the rinse area to be rinsed.
It is contemplated that a target rinse volume would result in the collection of 1 millimeter or less of fluid sample. It is also expected that not all samples collected in the field will need to be rinsed in the field. The rinsing can be performed based on a predefined trigger event, an external input, or based on some predefined schedule. Most often, such a trigger event will cause the system to collect a liquid sample from the ticket in the collection zone. However, it would be useful to include the ability to collect a liquid sample from a previously used ticket stored in the spent magazine. Such an ability would be useful, but is not required. Arrows in
There are a number of technological features and techniques that can be used to improve both the efficiency of the particle impaction process as well as the efficiency of particle removal after impaction. These features include the following:
It is contemplated that some embodiments of rinsing systems will beneficially incorporate combinations of the various methods discussed above. Having now discussed rinsing in general, specific examples will be provided, along with other sample retrieval techniques (i.e., non-liquid based retrieval).
An Exemplary Air Sampler with Means for Removing and Transferring Particulates from a Collection Surface to a Container:
Collection surface 534 can incorporate any of the coatings discussed above, or no coating. The configuration of collection surface 534 can include, but is not limited to, a plate, a disk, or an elongate tape. Preferably, collection surface 534 can be readily removed and replaced with a new collection surface either when the original collection surface is full, or particulates deposited on the collection surface require analysis.
Means 546 is employed to remove particulates collected on surface 534, and to transfer those particulates to a sample container 547. Specific examples of means 546 are described in greater detail below. Means 546 is operatively coupled to a control 538, which is also discussed in greater detail below.
Preferably, collection surface 534 is coupled to a prime mover 536 that moves the collection surface relative to virtual impactor 532 over time, so that particulates collected at different times are deposited on different portions of collection surface 534. It should be noted that prime mover 536 can instead optionally move virtual impactor 532, instead of, or in addition to, moving collection surface 534. It should be recognized that such a feature represents an additional functionality that is not explicitly defined with respect to the air samplers of
Referring once again to
Prime mover 536 is controllably coupled to a control 538. The purpose of control 538 is to control the movement of prime mover 536 to achieve the desired movement of either virtual impactor 532 or collection surface 534, and to actuate means 546 when a sample of particulates is to be transferred from surface 534 to container 547. Means 546 can be actuated based on the occurrence of a predefined condition (such as a sensor indicating that a triggering event has occurred), based on an affirmative user command, or according to a predefined sampling protocol. For example, an integrated system can be designed to deposit a plurality of spots during a given time period, where some of the spots are to remain on the collection surface, and others of the spots are to be transferred to a sample container.
It is contemplated that control 538 can be one of a computing device, an application specific integrated circuit (ASIC), a hardwired logic circuit, or a simple timing circuit. In at least one exemplary embodiment, software is executed to control the operation of the device, and the control includes a memory and a microprocessor. This software can include a program that determines the positioning of the collection surface relative to the minor flow. The software may also include a program that controls the schedule for taking environmental samples at predetermined times, thereby producing a spot on the surface at specific spaced-apart times. In addition, the air samplers disclosed herein may execute logic that modifies the sampling schedule in accordance with algorithms that are responsive to onboard sensors 540. Finally, the software can monitor the particulate collection, generating a log of the actual time when each sample is taken in association with the disposition of the spot deposited on an collection surface at that time. This log facilitates correlating a specific sample (i.e., a specific spot) with a particular moment in time at which the spot was deposited. Control 538 is shown as being controllably coupled to fan 533. According to one sampling protocol, fan 533 will operate continuously. According to another sampling protocol, fan 533 will operate for a predefined period of time while a spot is being deposited on the collection surface, and then will be de-energized by the control. The flow of fluid into the system can be interrupted between the deposition of samples that are deposited as spots, and when the collection surface is being replaced. It should be recognized that control 538 can be configured to implement a variety of different sampling and collection paradigms.
Empirical tests of a prototype device, functionally similar to system 530, and employing a polymeric tape as a collection surface, have confirmed the ability of a virtual impactor to deposit spots of particulates on a movable collection surface.
As noted above, in some embodiments, system 530 may beneficially include sensors 540, which communicate with control 538 to cause a sample to be collected in response to an event that is detected by the sensors (i.e., one or more sensors). For example, a collection system may be mounted in a smokestack of a manufacturing facility, to generate a collection record of emissions from the smokestack. Such a system might be equipped with a carbon monoxide monitor, and when levels of carbon monoxide are at a predetermined level (based on sensor data from sensors 540), controller 538 can be programmed to initiate a sampling event, to deposit particulates on the collection surface for later analysis in response to the sensor readings. Sensors can be used to measure relevant environmental factors that include, but are not limited to: pressure, humidity, temperature, particulate count, and the presence of a particular target bio-molecules (such as particular cell types, pathogens, and toxins). Based on the detection of a specific environmental factor by such a sensor, or in accord with a sampling protocol programmed into control 538, one or more of the following exemplary functions (as well as many others) can be executed by control 538: generate a record of the environmental conditions at the time of spotting; control the operation of any system component whose performance depends on a measured environmental parameters; manipulate a programmed sampling protocol based on measured environmental factors; actuate means 546 to transfer collected particulates to a sample container; and produce an alert signal (for example, by a radio transmission or a hard-wired signal transmission) to notify an operator of an important change in the environmental conditions (as determined by programmed control parameters).
Referring once again to
One or more optional detectors 544 can be included to analyze particulates deposited on the collection surface. It is expected, however, that the collection surface will most often be removed from the system before any of the particulates (i.e., spots) are analyzed. By using a separate detector, the cost of system 530 can be reduced, since detectors are often sophisticated and expensive. Furthermore, many detection methods require particulates comprising the spots to be removed from the collection surface before being analyzed. If detector 544 requires the particulates comprising the spots to be removed from the collection surface prior to their analysis, a particulate removal system (generally a liquid rinse directed at a specific spot) must also be incorporated. Particulates comprising the spots can also be removed by scraping, and with other means.
Preferably system 530 will often be used in a fixed (permanent) location to monitor a specific geographical location over a long period of time. Spent collection surfaces will be removed for storage and or analysis, and new collection surfaces can then be inserted into system 530. It is contemplated that system 530 can also be used as a survey instrument that is likely to be moved from one location to another, to collect samples at different geographic locations. Such a survey instrument can be used to obtain samples (spots) from many locations within a region (or at different regions) on a single collection surface. This feature has utility in determining the source of a particular contaminant and monitoring a number of locations when the spots on the collection surface are subsequently analyzed, although it should be recognized that an analytical component that is used with a system including the various samplers disclosed above, can be beneficially implemented in system 530 as desired.
While not specifically shown, it is further contemplated that system 530 can beneficially have the ability to communicate with a control system at a remote location, to send and receive control signals and communicate other data.
In many applications, it may be important that the system be able to sample a large volume of air (≧300 lpm), but that the sample collected be deposited in a small area (e.g., as spots ˜1 mm in diameter). To achieve these goals, it will be important to achieve the separation of particulates from a large air volume and their concentration in a relatively smaller air volume (i.e., the minor flow). In such applications, it is contemplated that two in-line stages of virtual impaction may be used. In the first stage, 90% of the inlet fluid is discarded, and the remaining 10% of the fluid (first stage minor flow) contains the desired particles. This first stage minor flow then enters a second virtual impactor stage, with 90% of fluid that enters the second stage being exhausted to the environment. Therefore, the two stages have the combined effect of concentrating the outlet minor fluid volume to 1/100th of the initial inlet flow volume. This relatively small minor flow should then be appropriate for depositing the concentration of particulates as spots onto a small surface area. The spot density on the surface should typically be as high as possible, without cross-sample contamination occurring, in order to minimize the required area of the collection surface.
Means for Transferring Particles from a Collection Surface to a Container: In several embodiments of the air samplers disclosed herein, a fluid is used to remove and transfer the particulates from the collection surface to a container. Depending upon the collector employed, the fluid can be a liquid or a gas.
Other elements of particle impact collector 625 include a fan 628, which is rotatably driven by an electric motor 630. Fan 628 impels fluid 610 in stream 621 toward coated impact collection surface 623. Other types of fans or impellers can alternatively be used. For example, a centrifugal fan (not shown) can be employed to move the fluid. If the fluid in which the particulates are entrained is a liquid, a pump (not shown) would be used instead of fan 628 to move fluid 610 toward coated impact collection surface 623.
To obtain a concentrated sample of particulates 614 from those collected on coated impact collection surface 623a, particle impact collector 625 preferably includes a specimen container 636 that is filled with a collected sample through a funnel 634. A liquid 638 that is rich in the particulates collected on the coated impact collection surface partially fills sample container 636. Liquid 638 is obtained by washing the particulates from the tape. A reservoir 642 is included to supply the liquid for this purpose. The liquid from the reservoir is conveyed through a fluid line 644 and sprayed toward tape 610 through a nozzle 646, which creates a fan-shaped spray 648 that washes the particulates from the tape. If necessary, a pump, e.g., a centrifugal or a peristaltic pump (not shown) may be used to force the liquid through nozzle 646 under sufficient pressure to wash away the particulates retained by the coated impact collection surface. These particulates are carried by a stream 650 of the liquid into funnel 634 and thus are conveyed into sample container 636. A relatively small volume of liquid can be employed, so as to avoid unnecessarily diluting the sample.
The material used for producing coated impact collection surface 623 and other coated areas or surfaces employed in other embodiments discussed herein for collecting particulates in accord with the concepts disclosed herein, is selected because of certain characteristics of the material that increase the efficiency with which the particulates are separated from the fluid in which they are entrained, and to enhance the removal of the particulates so that they may be transferred to a sample container. Each material used for a coating has certain advantages that may make it useful for separating a specific type of particulate from a specific type of fluid. For example, for use in particle impact collector 625, the TETRAGLYME material described above can be used for the coating. As noted above, this material is hydrophilic until it is exposed to water, and when dry, is relatively tacky, tending to readily retain particulates that impact it. Once water is sprayed onto the TETRAGLYME coated surface, the particulates that have been retained on the surface are readily released.
It should be recognized that collection/deposition substrate 623 is moved relative to the concentrated stream of particulates from the impactor over time, so that spots or samples of the particulates that have been collected on different portions of the collection/deposition substrate 623 correspond to different times at which the particulates were collected. Because the location of a “spot” of particulates deposited on the sample substrate (or collection/deposition substrate) is indicative of a time when the particulates were collected, the substrate can be made to move relative to the impactor, at least at spaced-apart times, to form spots of particulates (or continually, to form streaks of particulates). Moving the substrate at successive specific times permits multiple sample spots to be deposited on a single substrate without comingling the spots. The time at which each spot is deposited is associated with the spot. Alternatively, time can be linear in its association with a position of a particle as part of a streak of particles that are deposited continuously.
The integrated system embodiment of the concepts disclosed herein that are discussed above provide details indicating how a collection surface can be moved. It may generally be preferable that source 712 and the inlet used for directing particles toward the collection surface for collection not be disposed in substantially the same position. However, if both the inlet and source 712 are not operated simultaneously, such a configuration should not be a problem.
The fluid jet is directed at a selected group (or spot) of particles, which are “blasted” off the collection surface and into container 720. Container 720 should be properly positioned so that substantially all of the particles blasted from the collection surface are directed into the container. If desired, container 720 can be coupled in fluid communication with a vacuum source 722, so that particles are affirmatively drawn into container 720. Such a configuration reduces the likelihood of particles being dispersed in directions other than toward the sample container. Of course, a suitable filter must be employed to prevent the particles from escaping container 720 through the line that couples the vacuum source to the container. The angle at which fluid jet 718 is directed toward the collection surface should be selected to direct the blasted particles into the collection container.
When fluid jet 718 comprises a gas, the particles are transferred into the sample container without the use of any liquid, and no dilution of the sample has taken place. A further benefit of using a gas for the jet is that container 720 can be sealed and stored dry, so that a liquid is added only immediately before analysis of the sample stored in the sample container. This approach also reduces the weight of the sample, which can be important, particularly in an integrated system embodiment in which many samples are taken, since use of dry samples can significantly reduce the total weight of the samples. The gas selected for the fluid jet should be inert with respect to the particles collected, so that no undesired reactions occur between the sample particles and the gas. Preferred gases include compressed air, compressed nitrogen, compressed carbon dioxide, and inert gases such as argon.
When fluid jet 718 comprises a liquid, care should be taken not to use too much liquid, so that the sample of particles are not unduly diluted. Because of the energetic nature of the fluid jet, even a small amount of liquid is expected to be effective in transferring the particles from the collection surface and into the sample container.
A mechanical scraper 724 can be employed to remove and transfer selected particles 714 to container 720, as shown in the end view of
Another method of removing particles from scraper 724 without the use of a liquid rinse is to place the scraper in or immediately adjacent to container 720, and then to rapidly vibrate scraper 724, as is shown in
Instead of removing the particles from the collection surface, in some embodiments, the portion of the collection surface containing a specific spot of particulates is removed and placed into a container. In a first such exemplary embodiment, shown in
If the collection surface is easily cut (such as a thin fiber or plastic material), then pre-scoring may not be required. Particularly if the outer periphery of the punch is sharp, the punch will be able to remove un-scored portions of such a thin collection surface. The punch, or other member used to remove a portion of the collection surface, should not disturb the spot of particles on the collection surface.
The “punched” portion of the collection surface will fall into the container due to gravity. However, it may be useful for the container to be in fluid communication with a vacuum source as described above, to draw the removed portion into the container. A fluid jet 718 (preferably air) can be directed toward the cut portion of the collection surface to drive that portion into the container; however, such a jet has the potential to direct the particles in the spot in undesired directions (i.e., away from, rather than into, the container).
Note that a collection surface can be fabricated from a soluble material, such as starches or gelatin. When a portion of such a surface is placed into a container and a suitable liquid is added, the collection surface will dissolve, enabling the particles to freely disperse within the sample container. This technique can be quite beneficial, particularly in cases in which the presence of a portion of a collection surface in a liquid sample is not compatible with a particular analytical method.
It is contemplated that combinations of the above techniques can be useful. For example, a collection surface can be coated with a dissolvable coating, so that when a liquid jet is directed at that portion of the collection surface (see
Yet another variation, shown in
Suitable sample containers can be made of plastic, although glass, metal, and ceramic can alternatively be employed. As with any sample container used to collect a sample for analysis, containers should be inert and clean, so that contaminants are not introduced into the sample.
As noted above, the spotting nozzle directs a jet of gaseous fluid toward the impaction plate. The spotting nozzle (i.e., the acceleration nozzle) may be of various shapes, such as round or configured as a slit. A round acceleration nozzle includes a generally round outlet through which the gaseous fluid is directed. The nozzle body may be generally cylindrical. A slit-shaped acceleration nozzle includes a generally rectangular outlet through which the gaseous fluid is directed.
The impaction plate may take a variety of shapes, but the collection surface is typically flat. In some embodiments, the impaction plate is a disk, e.g., configured to be flat, thin, and circular. A disk axis extends perpendicularly through the center of the two generally parallel, circular shaped opposite surfaces of the disk. In such embodiments, the collection surface is on one of the two planar generally parallel surfaces of the disk, and can be spaced apart from the center (or from the disk axis).
The impaction plate can be made of a substantially homogenous material, although it is possible to embed or otherwise incorporate a collection surface of one material on an impaction plate made of a different material. The plate, or at least its collection surface, can be made of a material sufficiently durable to withstand repeated surface regeneration without incurring damage. Many materials are suitable for this purpose, including glass, quartz, ceramic, silicon, metal, and plastic. In addition, coatings used to increase the hardness and/or the resistance to abrasion of the material can be deposited on the material.
When detector 230 and light source 240 are disposed on opposite sides of the impaction plate, it should be recognized that the impaction plate (or at least that portion of the impaction plate where the nozzle deposits a spot of particles) should be formed of an optically transparent substrate. Exemplary optically transparent substrates comprise UV transparent materials such as fused silica, pure silica, and sapphire (available from Edmond Scientific Co.). However, when detector 230 and light source 240 are disposed such that light from the light source can reach the deposited particles, and light from the deposited particles can reach the detector without interference from the impaction plate, impaction plates comprising non-optically transparent substrates can be employed.
In an exemplary embodiment, the collection surface is substantially smooth. A smooth surface may be preferred since it can more readily be cleaned by the surface regenerator. On the other hand, particles tend to bounce off smooth surfaces more easily, thus decreasing collection efficiency. Consequently, in some embodiments, the collection surface has outwardly projecting structures, such as rods or ribs. For example, the collection surface can be micro-machined to incorporate pyramid-shaped structures of approximately 1 μm-10 μm in height and width. In these embodiments, particle loss is minimized, but relatively harsher surface regenerators are required for cleaning the collection surface.
One function of the impaction plate is to support the collection surface for the accumulation of a sample of airborne particles during impaction. Accordingly, at least at one point in the cycle of operation of the device, the collection surface is disposed adjacent to the spotting nozzle. Typically, the collection surface is horizontal while the spotting nozzle is vertical.
The surface regenerator is configured to regenerate the surface, i.e., to remove a spot or deposit of particles from the collection surface after analysis, and thus, to make the collection surface available for collecting another spot. The surface regenerator must remove substantially all of the spots from the collection surface, so that a prior use of the collection surface does not contaminate or otherwise interfere with analysis of samples comprising subsequently gathered spots.
In some embodiments, especially where a smooth collection surface is employed, a surface regenerator may comprise a felt or cloth pad that is pressed against a moving collection surface as it slides towards the nozzle. The term “felt” is intended to generally encompass any form of a porous fibrous structure, typically unwoven, created by interlocking fibers using heat, moisture, or pressure. Suitable fibers include, but are not limited to, polyester, polyurethane, polypropylene, and other synthetic and natural fibers. The term “cloth” is intended to convey a material that is made by weaving, felting, knitting, knotting, or bonding natural or synthetic fibers or filaments. Of course, movement of a pad relative to the collection surface while a force is applied may be achieved by many different means. Alternatively, a felt or cloth wheel may be employed, wherein a motor spins the wheel when it is in contact with the spot, thus cleaning and regenerating the collection surface. In other embodiments, the surface regenerator can be configured as a brush or blade that removes the spot, with a sweeping or scraping motion. When the collection surface is not smooth, one or more brushes are desirable, and their sweeping motion may be performed in multiple directions. In yet other embodiments, surface regeneration can be achieved by blowing a stream of fluid (such as air or a rinse liquid) at an angle toward the spot, i.e., the surface regenerator comprises a nozzle oriented an angle towards the collection surface, which blows a stream of fluid at high velocity towards the collection surface. In some embodiments, regeneration is aided by electro-statically charging the spot either before or during the action of the regenerator. The collection surface may be temporarily provided a positive charge, a negative charge, or alternating positive and negative charges. In some embodiments, the regenerator comprises at least in part, heaters or lasers capable of transferring energy to and heating the surface spot/collection surface. In some embodiments, multiple regenerators are included and are used sequentially in each cycle of the device, or periodically (i.e., a normal cleaning after each collection cycle, followed by periodic deep cleanings after each of a predefined number of collection cycles).
Some embodiments incorporate an optional size selective inlet 290 for preconditioning the air sample (i.e., the gaseous fluid) by removing particles above a desirable size (this element is generally consistent with the pre-filter discussed above in detail). A “size-selective inlet” removes particles above a certain size (aerodynamic diameter) from a stream or sample of gas. The term “remove” is intended to mean that for a predetermined particle size, about 50% of the particles are removed from the gas sample, and the remaining particles pass through the size-selective inlet. For particles of smaller sizes than the predetermined size, most, or almost all, particles pass through the inlet, while for particles of sizes larger than the predetermined size, most, or almost all, particles are removed. The substrate of a size-selective inlet collects the removed particles. In certain embodiments, a size-selective inlet comprises an inertial impactor. The size of the particles removed is determined, in part, by the velocity of the gas sample as it comes out of the acceleration nozzle. The higher the velocity, the smaller the size of the particles removed. Thus, by selecting the appropriate acceleration nozzle, a predetermined upper size of particles can be removed from a gas sample. In certain embodiments, a size-selective inlet can comprise a filter, an elutriator, or any other device capable of removing particles greater than a predetermined size. In at least one embodiment, the size-selective inlet removes particles above about 10 μm, but may be set to remove particles above other different sizes, for example, above about 12 μm, above about 15 μm, above about 20 μm, and above about 25 μm. In those embodiments where a virtual impactor is included, the size-selective inlet may be disposed either upstream or downstream of the virtual impactor. Removal of large airborne particles eliminates potential sources of interference with the optical detectors discussed above.
One exemplary embodiment providing for intermittent relative motion between the sample substrate and the adjacent stream of particulates is shown in
The nozzle directing the minor flow from the impactor toward disk 516 cannot be seen in
Disk 516 can be moved using an appropriate prime mover 520, such as a stepper motor. As shown, one embodiment includes a shaft 518 detachably coupled to disk 516 and driven by prime mover 520. It is contemplated that disk 516 will remain stationary for a desired time interval, and then will be rotated a sufficient amount to collect another distinct spot on the disk. The impactor can be cycled off during the movement if desired.
In another embodiment, the sample substrate (e.g., the disk) is continually moved at a fixed rate, resulting in annular rings defined by streaks of particles on the sample substrate, instead of discrete spots. The use of streaks somewhat simplifies the operation of the collector, in that it can operate continuously, rather than being cycled on and off.
Although the concepts disclosed herein have been described in connection with the preferred form of practicing them and modifications thereto, those of ordinary skill in the art will understand that many other modifications can be made thereto within the scope of the claims that follow. Accordingly, it is not intended that the scope of these concepts in any way be limited by the above description, but instead be determined entirely by reference to the claims that follow.
This application is based on a prior copending provisional application Ser. No. 60/700,228, filed on Jul. 18, 2005, the benefit of the filing date of which is hereby claimed under 35 U.S.C. §119(e). This application is further a continuation-in-part of prior copending U.S. patent application Ser. No. 11/385,326, filed on Mar. 21, 2006, and a continuation-in-part of prior copending U.S. patent application Ser. No. 11/380,634, filed on Apr. 27, 2006, both of which are continuation-in-parts of prior U.S. patent application Ser. No. 11/058,442, filed on Feb. 15, 2005, which itself is a continuation-in-part of prior U.S. patent application Ser. No. 10/366,595, filed on Feb. 11, 2003, which issued as U.S. Pat. No. 6,938,777 on Sep. 6, 2005, which itself is based on a prior provisional patent application Ser. No. 60/355,915, filed on Feb. 11, 2002, the benefit of the filing dates of which is hereby claimed under 35 U.S.C. §119(e) and 35 U.S.C. §120. U.S. patent application Ser. No. 10/366,595 is further a continuation-in-part of a prior patent application Ser. No. 09/955,481, filed on Sep. 17, 2001, now issued as U.S. Pat. No. 6,695,146, the benefit of the filing date of which is also hereby claimed under 35 U.S.C. §120. Still further, copending patent application Ser. No. 11/058,442 is also a continuation of prior conventional application Ser. No. 10/066,404, filed on Feb. 1, 2002, which issued as U.S. Pat. No. 6,887,710 on May 3, 2005, and which is based on a prior provisional application Ser. No. 60/337,674, filed on Nov. 13, 2001, the benefit of the filing dates of which is hereby claimed under 35 U.S.C. §119(e) and 35 U.S.C. §120. Conventional application Ser. No. 10/066,404 is also a continuation of a prior conventional application Ser. No. 09/775,872, filed on Feb. 1, 2001, which issued as U.S. Pat. No. 6,729,196 on May 4, 2004, and which is a continuation of a prior conventional application Ser. No. 09/265,619, filed on Mar. 10, 1999, which issued as U.S. Pat. No. 6,267,016 on Jul. 31, 2001, and Ser. No. 09/265,620, filed on Mar. 10, 1999, which issued as U.S. Pat. No. 6,363,800 on Apr. 2, 2002, the benefit of the filing dates of which is hereby claimed under 35 U.S.C. §120.
| Number | Date | Country | |
|---|---|---|---|
| 60700228 | Jul 2005 | US | |
| 60355915 | Feb 2002 | US | |
| 60337674 | Nov 2001 | US |
| Number | Date | Country | |
|---|---|---|---|
| Parent | 10066404 | Feb 2002 | US |
| Child | 11058442 | US | |
| Parent | 09775872 | Feb 2001 | US |
| Child | 10066404 | US | |
| Parent | 09265619 | Mar 1999 | US |
| Child | 09775872 | US | |
| Parent | 09265620 | Mar 1999 | US |
| Child | 09265619 | US |
| Number | Date | Country | |
|---|---|---|---|
| Parent | 11385326 | Mar 2006 | US |
| Child | 11458364 | US | |
| Parent | 11058442 | Feb 2005 | US |
| Child | 11385326 | US | |
| Parent | 10366595 | Feb 2003 | US |
| Child | 11058442 | US | |
| Parent | 09955481 | Sep 2001 | US |
| Child | 10366595 | US |
