There is a need for a low cost, fast response, low detection limit, low false alarm rate, bio-aerosol early warning system for use in governmental and commercial infrastructure protection initiatives. Unfortunately, current individual technological approaches to bio-detection often must make trade-offs among cost, speed of response, sensitivity, and accuracy. For instance, the “gold standard” for pathogen identification, the polymerase chain reaction (PCR) bioassay, is very accurate but requires expensive biochemicals. On the other hand, low-cost-to-operate aerosol sample collectors coupled with real-time, non-selective light scattering detectors yield an unacceptable number of false alarms.
A potentially revolutionary solution to this problem is the coupling, or integration, of two or more, low cost, orthogonal sensor triggers together with a very accurate bioassay. One example of such a sensor trigger are fast aerosol light scattering detectors. By themselves, light scattering detectors produce many false positive signals. However, when coupled to a second, orthogonal trigger, the likelihood that the two sensors produce false positive signals at the same time is acceptably small. Furthermore, since the bioassay need be run only in those occasions when the multiple orthogonal sensor triggers produce a positive signal, the costs to operate the systems are greatly reduced while maintaining a high degree of accuracy. Moreover, additional reductions in cost may be achieved by miniaturizing the triggering and bioassay devices such that smaller amounts of reagents are consumed together with a corresponding reduction in waste produced waste. A large, laboratory-based research effort based on microfluidic insulator-based dielectrophoresis (iDEP) at our facilities over the past 7 years has shown that iDEP is capable of trapping and differentiating different types of bioparticles (live vs. dead bacteria; spores vs. vegetative cells) under low flow conditions. We have applied this experience to the development and laboratory testing of a prototype iDEP triggering device.
To accomplish our objective, we have applied experience in developing microfluidics and iDEP technology at our facilities and described and disclosed in U.S. Pat. Nos. 7,347,923, 7,204,923, and 7,014,747, herein incorporated by reference in their entirety. Additionally, iDEP technology is further disclosed by Lapizco-Encinas et al. in “Dielectrophoretic concentration and separation of live and dead bacteria in an array of insulators,” Analytical Chemistry, 2004, v. 76(6): pp. 1571-1579; in “Insulator-based dielectrophoresis for the selective concentration and separation of live bacteria in water,” Electrophoresis, 2004, v. 25(10-11): p. 1695-1704; and in “An insulator-based (electrodeless) dielectrophoretic concentrator for microbes in water,” Journal of Microbiological Methods, 2005, v. 62(3), SI, pp. 317-326; and by Simmons et al., in “Polymeric insulator-based (electrodeless) dielectrophoresis (iDEP) for the monitoring of water-borne pathogen,” Royal Society of Chemistry, Special Publications, 2005, iss. 297; pp. 171-173; by Davalos et al. in “Performance impact of dynamic surface coatings on polymeric insulator-based dielectrophoretic particle separators,” Analytical and Bioanalytical Chemistry, 2008, v. 390(3): pp. 847-855; and by Sabounchi et al. in “Sample concentration and impedance detection on a microfluidic polymer chip,” Biomedical Microdevices, 2008, v. 10(5): pp. 661-670, all herein incorporated by reference. Ancillary microfluidic components (valves, fittings, pumps, etc) and the high flow plastic microfluidic devices needed for this project were also previously developed at our facilities.
The present system comprises a “smart” system for unattended particle collection capability that would include the capability to autonomously trigger a subsequent analysis for microchemical/biological species. The device further includes a compact, efficient aqueous sample collector; an insulator-based dielectrophoretic (iDEP) device for particle concentration and trapping, and a laser induced fluorescence detection device to trigger an electronic response in the device to direct the instrument to begin a more detailed analysis of the trapped particles using a complimentary microanalysis system for fast, accurate presumptive identification. Also included is a sample cleanup capability to flush the microfluidic chip of collected debris and thereby provide for re-use of the chip.
This device will classify particles collected from the surrounding atmosphere by first screening the particles to accept only those within a specific size range of diameters and secondly by accepting only those particles that have been trapped in dielectrophoretic fields having specific predetermined voltage potentials such that the device triggers the use of a downstream bio-identification assay. Should this instrument trigger not signal a “positive” result, no further analysis is performed.
The accompanying drawings illustrate one or more embodiments of the present invention and, which together with the description, form a part of the specification and serve to explain the principles of the invention. These drawings are only for the purpose of illustrating one or more preferred embodiments of the invention and are not to be construed as limiting the invention. In the drawings:
In iDEP systems of our design, electrodes located outside the microfluidic chip apply an electric field across the main fluidic channel. Insulating posts and other features in the chip cause non-uniformities in the electric field and any particle traveling in a fluid inside the chip experiences dielectrophoretic forces and these forces can be used to trap, concentrate, and separate particles such as spores, cells, or viruses under low flow conditions.
The present system comprises the following subsystems:
Fluidics: to transport fluid from an aerosol sample collector, through the iDEP chip, through the detector, and out to the waste bottle. The fluidic system also allows the introduction of particles from a separate sample vial into the fluid that comes out of the aerosol sample collector.
Electronics: to control and monitor the aerosol sample collector, valves, pumps, particle detector, and pressure sensors.
Control software: to input the operating parameters for either a manual run or a fully automated run.
Particle detector: for providing an indication of whether or not particles have been trapped by the iDEP chip.
Packaging: an enclosure to protect the instrument that allows for air to be processed by the aerosol sample collector.
Each of these subsystems is now described in more detail below.
Fluidics:
An important lesson learned during development of the iDEP system was that since the system was used to trap and manipulate particles, clogging of the tubes carrying particle suspension in and out of the iDEP chip by the particles was an issue. It was eventually decided that very small capillary tubing (e.g. plastic capillary tubing that is 360 μm outside diameter (O.D.), 175 μm inside diameter (I.D.) should only be used in an iDEP system when it was absolutely necessary to minimize both time to travel a certain length and particle dispersion. Thus
As shown in
Electronics:
A commercial USB capable compact DAQ (cDAQ) system (obtained from National Instruments Corporation, Austin, Tex.) was used as the main data collection and control interface. This modular system allowed specific modules to be easily installed and configured through LABVIEW®. The cDAQ performs all of the required digital input and output functions, as well as 16 bit analog I/O. The digital output is capable of controlling eight 3-way fluidic valves. Valve control requires that a custom interface box be made, which incorporates H-bridge driver circuitry, i.e., an electronic circuit which enables a voltage to be applied across a load in either direction. These circuits are often used to operate a DC motor in both the forwards and backwards direction. Analog signal feedback provides valve status. In addition, the cDAQ monitors sensors and control system components. A control diagram of the system is shown in
Control Software:
A new LABVIEW®-based control software for the National Instruments cDAQ system described above was created and is illustrated in representative screen shots shown in
Particle Detector:
Four different particle detector types were evaluated.
Capillary based impedance detector: This was carried out using a Capacitively Coupled Contactless Conductivity Detection instrument (C4D, manufactured by eDAQ, Australia, www.eDAQ.com). In the C4D instrument, a glass capillary tube carrying the sample out of the iDEP chip is passed through two annular electrodes separated by a ground plane (
Through-capillary absorbance spectrometer: A UV-visible light single wavelength spectrometer (Thermo Finnigan) was incorporated into the iDEP system and the fluorescence signal was recorded by the LABVIEW®-based control program (
On-chip fluorescence spectrometry: An SVM340 portable microscope (LABSMITH™) shown in
Off-chip, capillary-based based fluorescence spectrometer: A Sandia designed custom off-chip, modular, capillary-based laser induced fluorescence (LIF) spectrometer, such are disclosed in commonly owned U.S. Pat. Nos. 6,998,598 and 7,452,507, herein incorporated by reference, is shown in
Packaging:
The system was ruggedized for transport and final integration and testing at both the lab and at the public venue. Brackets were fabricated to secure all components firmly to the base plate. The entire system will fit in a compact 19.5″×20″×11″ enclosure. The system requires one standard 120V 15 A outlet for power. The finished Field Test Unit 1 is shown in
The iDEP chips, shown schematically in
It was found that when first produced, the iDEP chips did not comprise a surface chemistry that would prevent or at least minimize particles from clogging and fouling the fluid channel as seen in
It has also been necessary to adjust the pH of the background buffer to pH8 while simultaneously keeping its conductivity low. Trapping has been demonstrated with 0.001% TWEEN® 20 (a polyoxyethylene derivative of sorbitan monolaurate obtained from the Promega Corporation, Madison, Wis.). Other TWEEN compositions may be possible but were not attempted. It would be expected that a different surfactant concentration would be needed if other TWEEN compositions were used. It is important to demonstrate trapping in the presence of TWEEN® 20 as this is the additive present in the water used by the aerosol sample collector. TWEEN® 20 prevents fouling of the aerosol sample collector components and increases the collection efficiency of the aerosol sample collector. In addition, TWEEN® 20 containing water solutions are used to flush out and clean the iDEP chips between runs.
The inlet and outlet electrodes, shown in
The optimal way to introduce the sample into the iDEP chip was empirically determined as shown in
After further experimentation and modifications to the fluidic architecture, some trapping was achieved by first injecting the sample (50 μL/minute, 200 μL total volume) and then the buffer (3 tit/minute) through the ground inlet electrode-port and flowing all of the fluid out through the non-energized outlet port (see
In the final, successful configuration (see
Trapping and Detection:
When in use, the background buffer (also pH8 DI water with 0.001% TWEEN® v/v) was flowed through the inlet electrode and through the rest of the system for about a minute at 3 μL/minute using a stepper motor, microprocessor-controlled pump such as a MILLIGAT® pump (available from Global FIA, Inc. Fox Island, Wash., USA) comprising a miniature pump/motor/gear assembly, a micro-electric controller, and a linear power supply. In order to begin trapping particles, a portion of the fluid sample generated by the aerosol collector is introduced into the fluid stream and thus into the fluid pump where it is directed into the iDEP chip. The voltage at the inlet electrode of the iDEP chip is initially set to Ground (done to avoid the leakage of voltage upstream to the metal MILLIGAT® pump) and the outlet electrode set to a predetermined negative potential, e.g., ˜−1600 V. The range of voltage potentials necessary to trap any specific particle species, e.g., pathogenic spores or bacteria, would need to be determined experimentally since, presumably, the optimal trapping potential for each would be different. Initially, the system would be set up to investigate voltage ranges which were most effective at trapping particles of interest, e.g., pathogens and the like. In actual use, therefore, the device potentials would be preset to scan specific ranges of voltage in an either ascending or descending protocol and thereby incrementally step through the range of voltages found to be important for diagnostic inspection. At each level, the voltages are held constant at the pre-set values for 30 seconds in order to achieve particle trapping within the system, assuming that particles having the targeted trapping characteristics are present within the sample. After the 30 seconds, the trapping phase was completed and the voltages of both the inlet and outlet electrodes were set to Ground and the cycle begun again at an incremented potential.
In a typical trapping experiment 200 microliters of beads or of Bacillius globigii (Bg) spores (106 particles/ml suspended in pH8 deionized (DI) water with 0.001% TWEEN® v/v) labeled with fluorescein isothiocyanate (FITC) were injected into the inlet electrode before any voltage was applied.
Finally, in order to automate the detection and allow for unattended operation in the field, four detector technologies were evaluated.
In doing so, it was discovered that off-chip, capillary-based impedance and absorbance detectors were affected by iDEP-trapping related artifacts (
An inverted fluorescence video microscope (a SVM340 microscope available from LABSMITH™, Inc., Livermore, Calif.) was used to analyze the fluorescence signal during and after experiments. The microscope software allows the user to optimize the signal to noise ratio of the fluorescence intensity analysis by drawing analysis areas on the computer microscope viewer. Only the fluorescence data in those areas are integrated over time.
The SVM340 based on chip fluorescence detection was not affected by iDEP artifacts. This technique senses the trapping and concentration of particles between the posts. Since the particles are trapped between the posts as soon as the voltage is turned on, the detector responds within seconds of turning on the trapping voltage. Unfortunately, the optics of the SVM340 detector are not sufficiently robust to interrogate the chip for particles that did not carry a fluorescent tag; and while it is possible, in principle, to detect biological particles using native fluorescence, such an approach would require a modifying the chip and chip holder to include a fiber optic conduit for directing the needed excitation light and for returning the excited fluorescent signal from the particles trapped within the chip, and to provide for optical transparency above or below the chip's trapping region. This latter condition would likely require the chip and/or chip cover to be fabricated from fused silica or quartz.
While the three foregoing detection techniques could not be adapted to provide unattended operation the system was successfully operated using an off-chip laser induced fluorescence technique.
It will be appreciated that as soon as the trapping voltage is turned on, the fluorescence signal at the off-chip detector first instantaneously increases before beginning to rapidly decrease. We hypothesize that the first response is due to the electrokinetic forces accelerating the particles near the detector due to the applied electric field and the second response is an indication of containment initiation of a majority of the particles contained in the fluid up-stream in the iDEP chip. Trapping, therefore, is confirmed about a minute after the voltage to the electrodes in the iDEP chip is turned ON by a decrease in detected signal below an average background baseline level of the fluorescence signal count. The one minute delay in response is presumed to be caused by the time taken for the fluid to travel from the trapping region on the iDEP chip to the LIF sensor located about 2 inches away from the chip. That is, after the trapping voltage is turned ON, particles are immobilized within the post region of the iDEP chip while the fluid formerly containing the trapped particles, continues moving eventually leading to a particle depleted region of fluid reaching the detector. A minute after the trapping voltage is turned OFF, particles are once again detected as the fluorescence signal returns its average base-line count rate detected before trapping.
Lastly, we found that the off-chip LIF detector was not capable of detecting an iDEP induced increase in the concentration of particles. It was only capable of detecting the trapping and the release of the particles. This is due mainly because as the concentrated particles are released, they travel from the restricted fluid volume between the posts having a total cross-section of about 6,000 μm2 to the open channel having cross-section of about 5× as great and then into the 150 μm diameter capillary having a cross-section of 17,670 μm2. Furthermore, the Peclet number in the capillary decreases by a factor of 3 and so diffusive mixing is increased downstream as the particles travel approximately 60 millimeters (˜2¼ inches) to the off-chip fluorescence detector.
The iDEP system has been run repeatedly in the lab. iDEP chips can be reused 5 to 10 times before fouling after which a simple high flow background buffer injection is used to clean and reset the chip. The packaging and assorted electronic and mechanical components that make up the system are robust and reliable. As currently configured the iDEP system can be operated for up to eight hours unattended before needing to be serviced.
Having thus described an exemplary embodiment of the present invention, it should be noted by those skilled in the art that the disclosures herein are exemplary only and that various other alternatives, adaptations, and modifications may be made within the scope of the present invention. Accordingly, the present invention is not limited to the specific embodiments as illustrated herein, but is only limited by the following claims.
Finally, to the extent necessary to understand or complete the disclosure of the present invention, all publications, patents, and patent applications mentioned herein are expressly incorporated by reference therein to the same extent as though each were individually so incorporated.
This application claims priority to prior U.S. Provisional Patent Application Ser. No. 61/184,334 originally filed Jun. 5, 2009 entitled “System for Particle Concentration and Detection” from which benefit is claimed.
The United States Government has a paid-up license in this invention and the right in limited circumstances to require the patent owner to license others on reasonable terms as provided for by the terms of contract No. DE-AC04-94AL85000 awarded by the U.S. Department of Energy to Sandia Corporation.
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Number | Date | Country | |
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61184334 | Jun 2009 | US |