Method of Identifying Biologic Particles
20210123851 · 2021-04-29
Assignee
Inventors
Cpc classification
B01L2200/0652
PERFORMING OPERATIONS; TRANSPORTING
B01L2300/0627
PERFORMING OPERATIONS; TRANSPORTING
B01L2200/0647
PERFORMING OPERATIONS; TRANSPORTING
B01L2300/0864
PERFORMING OPERATIONS; TRANSPORTING
B01L3/502715
PERFORMING OPERATIONS; TRANSPORTING
B01L2300/087
PERFORMING OPERATIONS; TRANSPORTING
B01L3/502761
PERFORMING OPERATIONS; TRANSPORTING
International classification
B01L3/00
PERFORMING OPERATIONS; TRANSPORTING
Abstract
A method of analysing and identifying particles in an input fluid by electrical field analysis preferably in combination with imaging analysis and towards establishing characterises of the particles that can be compared with characteristics of known particles, preferably biologic particles such as bacteria and viruses. Preferably in a focusing step, the particles are focused as in a microfluidic particle sorting cartridge followed by electrical field analysis to determine impedance data. Preferably, the electrical field analysis is carried out in a water and alcohol solution.
Claims
1. A method of identifying biologic particles in an input fluid comprising: a focusing step in which the input fluid is sorted into a focused fluid stream including particles from the input stream in a desired range of particle sizes and/or a desired range of particle shapes, an imaging analysis step of determining with a first electromagnetic imaging apparatus image characteristics of the particles in the focused fluid stream, an electrical field analysis step of determining with an electrical field measurement apparatus electrical field characteristics of the particles in the focused fluid stream, using an image identification method comprising a review of the image characteristics to determine a primary estimated identity of the particles in the focused fluid stream as a primary probability profile of one or more known biologic particles, estimating an estimated concentration of the particles in the focused fluid stream when the electrical field characteristics is determined, using an electrical field identification method to estimate a secondary estimated identity of the particles in the focused fluid stream as a secondary probability profile of one or more known biologic particles based on the determined electrical field characteristics and the estimated concentration, and using the primary estimated identity and the secondary estimated identity to estimate a final estimated identity of the particles in the focused fluid stream as a final probability profile of one or more known biologic particles.
2. A method as claimed in claim 1 including creating image characteristics of the known biologic particles from images of the known biologic particles and recording the image characteristics of the known biologic particles in an image characteristics reference database and wherein the review comprising an image characteristics comparison step of comparing the one or more image characteristics of each separate particle of the particles with image characteristics of the known biologic particles in the image characteristics reference database, and an image characteristics identification step of identifying each separate particle as being one or more of the known biologic particles based on the results of the image characteristics comparison step.
3. A method as claimed in claim 2 wherein identifying each separate particle as being the one or more of the known biologic particles based on the results of the image characteristics comparison step comprises selecting one or more of the known biologic particles based on a determination as to the image characteristics of the known biologic particles that are closest to the image characteristics of each separate particle.
4. A method as claimed in claim 3 wherein the electrical field identification method comprising: i. creating correlated field/concentration data for a particle comprising: (a) one or more of the electrical field characteristics of the particle, and (b) the estimated concentration of particles in the focused fluid stream when the one or more of the electrical field characteristics for that particle is measured.
5. A method as claimed in claim 4 creating a field/concentration reference database of the known biologic particles by creating correlated filed/concentration data of the known biologic particles by use of the electrical field identification method for particles of the known biologic particles comprising: i. creating correlated field/concentration data for particles of the known biologic particles comprising: (a) one or more of the electrical field characteristics of the particles of the known biologic particles, and (b) the estimated concentration of particles of the known biologic particles in the focused fluid stream when the one or more electrical field characteristics for each particle of the known biologic particles is measured; recording correlated filed/concentration data of the known biologic particles in the field/concentration reference database as the correlated filed/concentration data of the known biologic particles, creating correlated field/concentration data for each separate particle of the particles of: (a) one or more of the electrical field characteristics of each separate particle, and (b) the estimated concentration of the particles in the focused fluid stream when the one or more electrical field characteristics for that each separate particle is measured, a field/concentration comparison step of comparing for each particle the correlated field/concentration data of the electrical field measurements and the estimated concentration for each separate particle with correlated field/concentration data of electrical field measurements and concentration of the known biologic particles in the field/concentration reference database, a field/concentration identification step of identifying each separate particle as being one or more of the known biologic particles based on the results of the field/concentration comparison step.
6. A method as claimed in claim 5 wherein identifying each separate particle as being one or more of the known biologic particles based on the field/concentration comparison step comprises selecting one or more of the known biologic particles based on a determination as to the field/concentration data of the known biologic particles that is closest the field/concentration data of each separate particle.
7. A method as claimed in claim 6 wherein: the electrical field analysis step includes subjecting the fluid to impedance spectroscopy to determine for a particle of the particles in the fluid Base Impedance/Frequency Data regarding the relationship of impedance vs frequency of the fluid containing the particle, the estimating of the estimated concentration of the particles in the focused fluid stream on which the Base Impedance/Frequency Data are determined, the electrical field identification method includes: (i) performing a first mathematical analysis step to the Base Impedance/Frequency Data including a first derivation analysis to provide First Derivate Impedance/Frequency Data, (ii) subjecting the First Derivate Impedance/Frequency Data to a second mathematical analysis step including a second derivation analysis to provide Curvature Data, and (iii) correlating the estimated concentration and the First Derivate Impedance/Frequency Data to provide Curvature/Concentration Data for the particle as the correlated field/concentration data.
8. A method as claimed in claim 7 wherein the field/concentration comparison step including comparing the Curvature/Concentration Data for the particle in the input fluid with Curvature/Concentration Data created for the known particles.
9. A method as claimed in claim 6 wherein the field/concentration reference database of the known particles includes Curvature/Concentration Data created for the known particles, creating the Curvature/Concentration Data created for the known particles by subjecting the known particles to impedance spectroscopy to determine for a particle of the known particles in a focused fluid stream of the known particles Base Impedance/Frequency Data regarding the relationship of impedance vs frequency of the known particles, the estimating of the estimated concentration of the known particles in the fluid stream on which the Base Impedance/Frequency Data are determined, performing the electrical field identification method including: (i) performing a first mathematical analysis step to the Base Impedance/Frequency Data of the known particles including a first derivation analysis to provide First Derivate Impedance/Frequency of the known particles Data, (ii) subjecting the First Derivate Impedance/Frequency Data of the known particles to a second mathematical analysis step including a second derivation analysis to provide Curvature Data the known particles, and (iii) correlating the estimated concentration of the known particles and the First Derivate Impedance/Frequency Data of the known particles to provide Curvature/Concentration Data for the known particles as the correlated field/concentration data of fluid containing the known particles, recording the Curvature/Concentration Data for the known particles in the field/concentration reference database as the correlated filed/concentration data of the known biologic particles, the field/concentration comparison step including comparing the Curvature/Concentration Data for the particle in the input fluid with Curvature/Concentration Data for the known particles, the field/concentration identification step of identifying each separate particle as being one or more of the known biologic particles based on the results of comparing the Curvature/Concentration Data for the particle in the input fluid with the Curvature/Concentration Data for the known particles,
10. A method as claimed in claim 9 wherein identifying each separate particle as being one or more of the known biologic particles based on the results of comparing the Curvature/Concentration Data for the particle in the input fluid with the Curvature/Concentration Data for the known particles comprises selecting one or more of the known C particles based on a determination as to the Curvature/Concentration Data for the particle in the input fluid that is closest the Curvature/Concentration Data for one or more of the known particles.
11. A method as claimed in claim 1 wherein the known biologic particles are selected from the group comprising bacteria and viruses, and the desired range of particle sizes and/or the desired range of particle shapes is selected having regard to the selected known biologic particles, wherein, when the particles are bacteria the range of particle sizes in the range of 0.5 um to 10 um, or 0.5 um to 5 um, and when the particles are virus the range of particle sizes is in the range of 0.1 um to 1 um, or 0.5 um to 1.05 um.
12. A method as claimed in claim 10 wherein the known biologic particles are selected from the group comprising bacteria and viruses, and the desired range of particle sizes and/or the desired range of particle shapes is selected having regard to the selected known biologic particles, wherein, when the particles are bacteria the range of particle sizes in the range of 0.5 um to 10 um, or 0.5 um to 5 um, and when the particles are virus the range of particle sizes is in the range of 0.1 um to 1 um, or 0.5 um to 1.05 um.
13. A method as claimed in claim 1 wherein the electrical field identification method is impedance spectroscopy.
14. A method as claimed in claim 10 wherein the electrical field identification method is impedance spectroscopy.
15. A method as claimed in claim 1 wherein the first electromagnetic imaging apparatus comprises an optical microscope, the method including providing for electromagnetic detection based on optical or phase contrast microscopy.
16. A method as claimed in claim 1 wherein the input fluid comprises an alcohol water solution.
17. A method as claimed in claim 16 wherein the alcohol water solution consists of water and isopropanol.
18. A method as claimed in claim 16 wherein the alcohol water solution consists of water and isopropanol with the isopropanol comprising at least 40% by volume.
19. A method as claimed in claim 1 wherein the focusing step includes passing the input fluid through a microfluidic particle sorting cartridge to provide in a microfluidic analysis channel of the microfluidic particle sorting cartridge the focused fluid stream.
20. A method as claimed in claim 19 wherein the input fluid comprises an alcohol water solution consists of water and isopropanol with the isopropanol comprising at least 40% by volume.
Description
BRIEF DESCRIPTION OF THE DRAWINGS
[0358] Further aspects and advantages of the present invention will occur from the following description taken together with the accompanying drawings in which:
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DETAILED DESCRIPTION OF THE DRAWINGS
Imaging Characteristics Reference Database
[0380] Reference is made to
[0381] In accordance with the present invention, multiple sample fluids were created, each in solution of 70% by volume isopropanol and 30% water and each sample having one only of each known bacteria SA, CJ, EC and PA. As a first electromagnetic imaging apparatus, an optical microscope was used to determine for individual particles of the bacteria of the seven optical characteristics set out in Table ion
[0382] For example, the optical characteristic of Integrated Density was determined from a large number of samples and multiple determinations for each of SA, CJ, EC and PA which, for each, the data was analysed to develop, based on a probability and statistics analysis, a probability curve shown as a normal distribution or bell curve for each of the four bacteria illustrated as a respective bell curve 102 as shown on
[0383] The graph in
[0384] In the same manner that the bell curve 102 and the range line 104 were developed for Integrated Density for each of SA, CJ, EC and PA, the optical characteristic of the other six optical characteristics in Table 1 on
[0385] The data from this assessment of all of the seven optical characteristics and data derived therefrom including the bell curves and range lines was recorded and formed into an image reference database.
[0386] As an example referred to as Case A, the same microscope was operated to assess the optical characteristics a particle A of a bacteria selected from one of SA, CJ. EC and PA, by placing the bacteria particle A in a solution of 70% by volume isopropanol and 30% water by volume in a concentration of about 1.1×10.sup.5 per ml to create for the particle A data representative of each of the seven optical characteristics in Table 1 an estimated value for the bacteria for each of the seven optical characteristics.
[0387] Referring to
TABLE-US-00002 TABLE 2 Known Selected Bacteria Case A Parameter SA CJ EC PA Integrated Density 82% 6% 12% 0% Area Perimeter Circularity Aspect Ratio (AR) Solidity (Maximum) Feret's Diameter Linear Weighted Estimate (Total/7)
[0388] For each of the other seven characteristics for Case A similarly using the same microscope, an estimated value of each of the other seven characterises are determined, from which estimated value a vertical line is determined to intersect with a location point on the range line for each of the four bacteria on the appropriate of
[0389] These one or more algorithms can be created, selected and used to estimate the primary estimated identity of the bacteria A of Case A as being one or more or each of the bacteria of the selected known bacteria SA, CJ, EC and PA. One simple method is to use as an algorithm, a linear weighted average, for example, of the sum of each column in Table 2 divided by 7 which is shown on Table 2 as the last row labelled Linear Weighted Estimate. Other functions and algorithms may be used to estimate the primary estimated identity and experience from analysing known samples can be factored into any algorithms as, for example, to weigh certain characteristics more highly than others depending on various and selected of the data.
[0390] As another example referred to Case B, the same microscope was operated to assess the optical characteristics a particle of a bacteria B selected from one of SA, CJ, EC and PA, by placing the bacteria particle B in a solution of 70% by volume isopropanol and 30% water by volume in a concentration of about 1.4×10.sup.7 per ml to create for the particle B data representative of each of the seven optical characteristics in Table 1, an estimated value for the bacteria for each of the seven optical characteristics.
[0391] Referring to
TABLE-US-00003 TABLE 3 Known Selected Bacteria Case B Parameter SA CJ EC PA Integrated Density 0% 0 0% 100% Area Perimeter Circularity Aspect Ratio (AR) Solidity (Maximum) Feret's Diameter Linear Weighted Estimate (Total/7)
[0392] As was done for Case A, for Case B using the same methods as in Case A, for each of the other seven characteristics for Case B a determination is made as to the normalized probability that the unknown bacteria B represents each one of the respective bacteria SA, CJ, EC and PA for each respective characteristic and entered into Table 3. Subsequently the primary estimated identity of the bacteria B of Case B as a primary probability profile of one or more or each of the known bacteria SA, CJ, EC and PA is calculated in the same manner as in Case A, using one or more algorithms based on the normalized probability for each of the characteristics in Table 3.
[0393] In the examples of Case A and Case B, seven optical characteristics are measured and used in calculating the primary estimated identity. This is not necessary. One or more than one of these seven optical characteristics may be measured and used in calculating the primary estimated identity, and as well other optical characteristics may be measured and used towards calculating the primary estimated identity.
[0394] Reference is made to the table of
[0395] To develop the data for
[0396] Individual test samples of each of the six selected known bacteria were created by placing the one bacteria in a solution of 70% by volume isopropanol and 30% water by volume. The optical camera was operated to assess the optical characteristics of a number of such cross test samples to create cross-test data representative of each of the seven optical characteristics. The selected algorithm was utilized so as, based on the cross-test data, to estimate the primary estimated identity as a primary probability profile that the tested bacteria is one or more of the six selected known bacteria. The results of the testing and analysis of the cross-test samples are shown on
[0397] The continued testing of groups of known bacteria using varying sorting apparatus, electromagnetic imaging apparatus, fluids, characteristics and algorithms to develop extensive Optical Characteristics Imaging Reference Databases, and then cross-testing the accuracy of the apparatus and methods against known bacteria, is a vehicle to select and enhance the apparatus and methods of the present invention.
Field/Concentration Characteristics
[0398] In accordance with the present invention, in a preferred arrangement, a fluid containing a particle in a “Particle Concentration” is subjected to impedance spectroscopy to determine for each particle in the fluid containing the particle “Base Impedance/Frequency Data” regarding the relationship of impedance vs frequency of the fluid containing the particle, The Impedance/Frequency Data is subjected to a first mathematical analysis step including a first derivation analysis to provide “First Derivate Impedance/Frequency Data”. The “First Derivate Impedance/Frequency Data” is subjected to a second mathematical analysis step including a second derivation analysis to provide “Second Derivate Impedance/Frequency Data”, herein referred to as “Curvature Data”. The “Curvature Data” is correlated to the “Particle Concentration” to provide “Curvature/Concentration Data”. The present invention at least in part arises in appreciating that the “Curvature/Concentration Data” for a particle provides a basis for distinguishing the particle from other particles, and preferably for assisting in the identification of the particle to develop the secondary estimated identity of a particle as a secondary probability profile of one or more known particles, as by comparing the “Curvature/Concentration Data” for a particle with “Curvature/Concentration Data” of known particles.
[0399] The first mathematical analysis step preferably involves subjecting the Impedance/Frequency Data to a first derivation analysis to produce Raw first derivation data which is preferably subjected to a soothing analysis to produce Smoothed first derivation data Preferably, the Smoothed first derivation data is analysed to identify one or more selected criterion and as a function of the one or more criterion a portion of the smoothed first derivation data is selected and subjected to the second derivation analysis to produce the Curvature Data.
[0400] The method preferably includes creating a field/concentration reference database of selected known particles by creating the Curvature/Concentration Data of the selected known particles and recording the Curvature/Concentration Data of the selected known particles in a field/concentration reference database. Comparison of the Curvature/Concentration Data determined for an unknown particle in a comparison step is compared to the Curvature/Concentration Data of the selected known biologic particles in the field/concentration reference database towards assisting in determining if there is any relationship or similarity.
[0401] Reference is made to
[0402] Multiple sample fluids were created each in solution of 70% by volume isopropanol and 30% water and each sample having one only of the known bacteria Escherichia coli (E. colis), Pseudomonas aeruginosa (Pseudos), and Staphylococcus aureus (Staphs) in a different known concentration. As an electromagnetic imaging apparatus, an impedance spectrograph was used to determine for individual particles of the bacteria in each sample the magnitude of impedance at multiple different frequencies. The magnitude of impedance is in units of ohms. The frequency is in Hertz.
[0403] The data representing the magnitude of impedance at multiple different frequencies for the samples with different concentrations of E. colis are shown in
[0404] The data of
[0405] The data of
[0406] On
[0407] On
[0408] The data for the selected portion of each plot line on
[0409] Reference is made to
[0410] Reference is made to
[0411] In accordance with the present invention, the data of
[0412] As one example referred to as Case C, a sample of an unknown bacteria is provided in a solution of 70% by volume isopropanol and 30% water by volume. For this sample of Case C, the Concentration of the Case C sample is determined by known methods. The Curvature for the sample of Case C is determined by the same methods used to determine the Curvatures for the samples in
[0413] As another example referred to as Case D, a sample of an unknown bacteria provided in a solution of 70% by volume isopropanol and 30% water by volume. For this sample of Case D, the Concentration of the Case D sample is determined by known methods. The Curvature for the sample of Case D is determined by the same methods used to determine the Curvatures for the samples in
[0414] The probability assessment based on the impedance analysis data and the determination of concentration in accordance with the present invention can be used to make a determination as to the secondary estimated identity of a bacteria, represented by the secondary probability profile that the unknown bacteria may be selected from one or more of the selected known bacteria and/or not one or more of the selected known bacteria. The probabilities of each of Case C and Case D provide for their samples what may be considered and is referred to as the second estimated identity from the electrical field identification method of the invention.
[0415] The probabilities of each of Case A and Case B provide for their samples what may be considered as the primary estimated identity from the image identification method of the invention discussed earlier.
[0416] The method of the invention involves using the primary estimated identity from the image identification method in combination with the second estimated identity from the electrical field identification method for the same samples to estimate a final estimated identity of the bacteria in those same samples, preferably as a final probability profile of the one or more known bacteria. Assuming that, for example, Case A and Case D are, for the same sample, then primary estimated identity is that the unknown bacteria has a primary probability profile of 82% SA, 6% CJ, 12% EC and 0% PA, and the secondary estimated identity is that the unknown bacteria has a secondary probability profile of is either one of SA (Staphs) and PA (Pseudos) and not EC (E. colis.). This leads to a final estimated identity of the bacteria as most likely being SA. Another function for using the primary estimated identity probability in conjunction with the second estimated identity probability is to add to the 82% SA probability the 12% EC probability since the second estimated identity probability indicates that the bacteria is not E. coli.
[0417] In accordance with the present invention, for the same samples, the primary estimated identity is to be determined from the image identification method and the secondary estimated identity is to be obtained from the electrical field identification method and, as a function of the primary estimated identity and the secondary estimated identity, a final estimated identity is to be estimated. The function to use or combine the primary estimated identity and the secondary estimated identity may be based, for example, in statistical and probability analysis.
[0418] As seen on
[0419] As another example of an electrical field identification method of the present invention to determine the secondary estimated identity of particles as a secondary probability profile of three known bacteria, three samples of bacteria were prepared, each in a fluid of 70% isopropanol by volume and 30% water by volume, as follows:
[0420] 1. E. colis particles in a concentration of 1×10.sup.7,
[0421] 2. Staph particles in a concentration of 9×10.sup.6; and
[0422] 3. Pseudos particles in a concentration of 7.2×10.sup.6.
[0423] An impedance spectrograph was used to determine for individual particles of the bacteria in each sample the magnitude of impedance at multiple different frequencies referred to as Base Impedance/Frequency Data. The Base Impedance/Frequency Data was subjected to a standard mathematical derivation from which a First Derivative of the magnitude of impedance at multiple different frequencies was developed and then subjected to a mathematical smoothing operation using a 20 point averaging filter so as to smooth the data and to become the Smoothed First Derivative data represented by the different plot lines on
[0424] As can be seen on
[0425] While the methods of the present invention for distinguishing between known bacteria from Base Impedance/Frequency Data may in some circumstances of use alone identify bacteria with high probability, when such methods are used in conjunction with other methods, such as optical imaging of identification, the combination of methods can assist in improving the probability of identifying bacteria.
Touchless Hand Cleaning Dispenser
[0426] Reference is made to
[0427] As seen in
[0428] As best seen in
[0429] A microfluidic sorting and analysis unit 40 is schematically shown on
[0430] As seen on
[0431]
[0432] The imaging apparatus 80 is operated to determine image characteristics of the particles in the focused fluid stream passing through the analysis channel 70. The electromagnetic field measurement apparatus 90 is operated to determine the electrical field characteristics of the particles in the focused fluid stream passing through the analysis channel 70, preferably impedance measurements of the particles in the focused fluid stream in the analysis channel 70. In this simple first embodiment, the first electromagnetic imaging apparatus 80 is also used to determine the velocity of flow in the analysis channel 70 from which with knowledge of the cross-sectional area of the analysis channel 70, the volume flow of the fluid in the analysis channel 70 can be calculated. The first electromagnetic imaging apparatus 80 is also preferably to be used to count, with time, the number of particles passing through the analysis channel 70 such that, with knowledge of the volume flow of fluid with time, and the number of particles passing through the analysis channel 70 with time, the concentration of particles in the focused fluid stream in the analysis channel 70 can be estimated.
[0433] As seen on
[0434]
[0435] As seen on
[0436] As seen in
[0437] Reference is made to
[0438] The microfluidic unit 40 comprising the microfluidic chip 42 and the electronic chip 44 provides the various analysis apparatus as desired towards analyzing the fluid and particles in the fluid as they pass through the microfluidic cartridge 42 and determining data about the particles and the focused fluid stream. Such data as obtained from the from the first electromagnetic imaging apparatus 80 and the electromagnetic field measurement apparatus 90 is via the electronic chip 44 provided to the controller 50 and, thus, to the computer 54 permitting image identification and electrical field identification methods to be carried out and the identity of the particles to be estimated in accordance with the method of the present invention.
[0439] With the electronic chip 44 electrically connected to the controller 50, the controller 50 can control the operation of the first electromagnetic imaging apparatus 80 and the electrical field measurement field apparatus 90, as well as the dispenser 10, as desired. Data from these apparatuses is provided to the controller 50 and the controller 50 can, as may be desired, at least partially process the data and, as may be desired based on pre-set protocols alone and/or on feedback based on the data, control the operation of the dispenser 10 and the microfluidic unit 40. The data provided to the controller 50 may, to some extent, be processed within the controller 50 and/or may be provided by the communication unit 53 to the computer 54 which may process the data and provide feedback to the controller 50 such as data regarding operation of the dispenser 10 and the microfluidic unit 40.
[0440] The preferred embodiment of the microfluidic cartridge 42, shown in
[0441]
[0442] The microfluidic channel may provide, if desired, a splitting step of splitting a single analysis channel into a pair of parallel analysis channels, each having a focused fluid stream as the same composition as the other.
[0443] In an alternate cartridge, the microfluidic particle sorting channels may provide a first sorting separation into different branches at an upstream portion to provide, for example, two or more downstream channels having particles in different ranges of size or shape and the sorting process may then be repeated with one or more of the initial downstream channels considered an upstream channel which is then sorted into a plurality of downstream channels containing particles further divided by range of size.
[0444] In the preferred embodiment illustrated, the microfluidic unit 40 has its electronic chip 44 hardwired to the controller 50 of the dispenser 10. This arrangement can advantageously provide for substantially all the processing to be provided in the controller 50 of the dispenser 10 and for power to be provided by the power source 51 of the dispenser 10. Such an arrangement is not necessary, for example, the electronics chip 44 may be provided to have one or more of its own: separate power source, processor or controller and/or communication units with, as one example, the electronic chip being independent and not hardwired to the dispenser 10 and, for example, communicating wirelessly either with a communication unit in the dispenser 10 or directly with the remote computer 54 or both.
[0445] Since data regarding the operation of the dispenser 10 is relevant data towards operation and control of the microfluidic unit 40, there preferably is provision for least some communication of data between the dispenser 10 and the microfluidic unit 40, albeit, this could be conducted through the remote computer 54. A communication unit on the chip 44 may preferably be provided merely to communicate with the dispenser 10 and this communication could be wirelessly.
[0446] Having at least some processing capability on the microfluidic unit 40 may well be preferred as contrasted with having all the processing capabilities in the dispenser 10 and/or the computer 54.
[0447] Each of the microfluidic unit 40, the dispenser 10 and/or the computer 54 may have a capability to store data.
[0448] The large databases and extensive processing expected to be required to carry out the identification methods preferably would have databases to store data on the computer 54 and the identification methods carried out on the computer 54, although this is not necessary.
[0449] In the first embodiment, the microfluidic cartridge 42 is provided as a separate unit incorporating the microfluidic particle sorting channel 60, the electrodes 91, 92, 93 and 94, the light emitter 81 and the light sensor 82 which is removably coupled, on one hand, to dispenser 10 via the outlet opening 36 of the catch tray 32 and, on the other hand, to the electronic chip 44. The electronic chip 44 is shown hardwired to the dispenser 10 and preferably forms a permanent part of the dispenser 10. The electronic chip 44 preferably contains front end electronics that are required for the analysis apparatus that is for the first electromagnetic imaging apparatus 80 and the electromagnetic field measurement apparatus 90.
[0450] Providing the microfluidic cartridge 42 to be a replaceable component is advantageous as this permits the microfluidic channels which may become contaminated with usage over time, to be easily replaced without a need to replace the electronic chip 44. As well, minimizing the extent to which any electronic components are permanently attached to the microfluidic cartridge 42 reduces the cost of the microfluidic cartridge 42 and replacement the microfluidic cartridges. Insofar as any electronic components as for the first electromagnetic imaging apparatus 80 and the electromagnetic field measurement apparatus 90 can be removably coupled to the microfluidic cartridge 42 for reuse is advantageous. In the first embodiment, the electronic components of the first electromagnetic imaging apparatus 80 and the electromagnetic field measurement apparatus 90 carried on the microfluidic cartridge 42 as contrasted with the electronic chip 44 have been minimized.
[0451] The microfluidic channels may preferably be subjected to cleaning so as to extend the time that the microfluidic cartridge 42 can be used without replacement. In the preferred embodiment, to clean the cartridge 42, the dispenser 10 may be operated without a person's hands being present in the dispenser 10 such that fluid will be dispensed into the catch tray 32 and, with time, will be passed through the microfluidic particle sorting channel 60. With the fluid being cleaning fluid such as an alcohol water solution, cleaning of the microfluidic channel can occur particularly during periods of time when the dispenser 10 is not expected to be used.
[0452] In accordance with the present invention, it is preferred that fluid flow through the microfluidic cartridge 42 be provided by passive flow generation systems. However, in the alternative or in combination with a passive flow generation systems, a pump not shown may be provided to generate flow, that is, to force fluid in the sump of the catch tray through the channels of the cartridge. Such pumps may be of any practical nature including electronically operated micro pumps as are known to persons skilled in the art, and may be provides as on the microfluidic cartridge 42 or as a separate element. Such a pump may be particularly useful to assist in increasing flow rates as during cleaning.
[0453] The invention has been described with reference to various descriptions and preferred embodiments, many modifications and variations will occur to persons skilled in the art. For a definition of the invention reference is made to the following claims.