1. Field of the Invention
This invention relates to a method for concentrating particles or molecules and an apparatus thereof, and particularly to a method and apparatus capable of trapping and concentrating particles or molecules in the microfluid and applicable to bead-based molecular assays.
2. Description of Related Art
Field-induced polarization of particles and molecules is responsible for a variety of electric particle and molecular forces that permit particle manipulation, drive colloid self-assembly, and allow suspension characterization. In electrolytes, there is considerable evidence that double-layer conduction around the particle, normal charging into the double-layer of thickness λ, and other polarization mechanisms involving currents, ion fluxes, electro-osmotic convection, and charge storage in double-layers are the more dominant polarization mechanisms than dielectric polarization. These double-layer polarization mechanisms are confined to the thin double-layers (of 10-100 nm) but nevertheless involve space charges. Empirical evidence for such double-layer polarization mechanisms includes the prevalence of the relaxation time aλ/D in many impedance and dielectrophoresis measurements which requires a conducting Stern layer. However, these lumped conductivity models do not capture local charge accumulation (capacitance) effects at certain locations within the double-layer.
A fluid used in micro-channel is known as a microfluid. In the recent decade, a microfluid system develops quickly since advantages including fewer samples needed, high sensibility, low cost, and manpower and time saving can be achieved after the system is miniaturized. Therefore, the microfluid system has been applied extensively in various fields, particularly in the bio-related field. However, most bio-samples are more precious and often have lower concentrations than the concentration of detection limit of the microfluid system. Accordingly, it is necessary to find a suitable micro-concentrating system to increase the concentration of the samples to the detection limit, so as to enhance the applicability of the microfluid system.
With these and other objects, advantages, and features of the invention that may become hereinafter apparent, the nature of the invention may be more clearly understood by reference to the detailed description of the present invention, the embodiments and the several drawings herein.
The present invention provides a method and apparatus to concentrate particles or molecules by capturing local charge accumulation effects at a certain location within the double-layer on the surface of a conducting granule, and the method and apparatus are able to apply to bead-based biomolecular assays.
The present invention discloses a method for concentrating particles or molecules, comprising the following steps. Firstly, a substrate comprising a reservoir may be provided and a conducting granule may be disposed in the reservoir. The conducting granule may be negatively charged or positively charged and comprise nano-pores or nano-channels permeable to ions. Then, an electrolyte solution may be disposed in the reservoir and the electrolyte solution comprises counter-ions having an opposite electric property to the conducting granule. Next, particles or molecules to be concentrated may be added into the electrolyte solution. The particles or molecules have an identical electric property as the conducting granule at a predefined pH value. Then, by driving the particles or molecules across the granule with an electric field, the pH of the electrolyte solution may be adjusted to the predefined value at a rate according to the pl value or pKa value of the particles or molecules. When applying an external electric field across the two side-channels, the counter-ions may enter the conducting ion-selective granule. After passing through the granule, counter-ions offset the charge on the granule surface at an ejecting pole and decrease the electric field locally. The electric lines will converge at the ejecting pole and result in tangential flux, which brings more ions into the pole area. Due to the low diffusion, the counter-ions will accumulate to produce high charge density and attract opposite charge (co-ions) nearby to maintain electric neutrality, both counter-ions and co-ions super-concentration phenomenon may come up. The charged particles or molecules can be concentrated in this fashion. The method may be applicable to the bead-based biomolecular assay. If the nano-pore or nano-channel size of the conducting granule is too small, usually less than the 3-5 times the double-layer thickness, counter-ions may be trapped in the granule, hence result in poor concentration phenomenon. Therefore, the pore size of the nano-pores or nano-channels may be roughly 3-5 times or larger the double-layer thickness, and the sizes of the particles or molecules can be nano-scale or micro-scale.
The present invention further discloses an apparatus for concentrating particles or molecules. The apparatus may comprise a substrate which may comprise a reservoir; a conducting granule which may be neither negatively charged or positively charged and comprise nano-pores or nano-channels able to permit ion permeation, and be disposed in the reservoir; an electrolyte solution which may comprise counter-ions having an opposite electric property to the conducting granule, and be disposed in the reservoir; and an external electric field which may be applied on the conducting granule. Wherein, particles or molecules to be concentrated have an identical electric property as the conducting granule at a predefined and desired pH value and be added into the electrolyte solution. When the particles and molecules are driven repeatedly through the granule by the electric field, the electrolyte solution may be adjusted to the predefined pH value at a rate according to the pl value or a pKa value of the particles or molecules. While the external electric field may be applied on the conducting granule, the counter-ions may exit from the nano-pores or nano-channels and have a nonuniform concentration on the surface of the conducting granule such that a transient ion super-concentration phenomenon may occur at an ejecting pole on the conducting granule so as to concentrate the particles or molecules. Additionally, the substrate may comprise a chip or a plastic plate, and the particles or molecules may comprise fluorescence dye particles or micro-colloid particles. The apparatus may be applicable to a bead-based biomolecular assay.
This present invention may involve a transient hundred-fold to million-fold concentration of double-layer counter-ions at the ejecting pole of a millimeter-sized conducting nano-porous granule that permits ion permeation by applying a high-intensity electric field across the apparatus. The higher the number of charges of the particles or a dissociation degree of the molecules in the electrolyte solution, a concentration effect of the particles or molecules is better. In addition, the concentration effect of the particles or molecules in independent of viscosity thereof.
The present invention also discloses the mechanism behind the transient ion super-concentration phenomenon at the ejecting pole and demonstrates that a two-order to six-order enhancement in the particle or molecule concentration may be achieved locally if the conducting granule is permeable to ions. The dynamic super-concentration phenomenon may be attributed to a unique counter-ion screening dynamics that transforms half of the surface field into a converging one towards the ejecting pole. The resulting surface conduction flux may then funnel a large upstream electro-osmotic convective counter-ion flux into the injecting hemisphere towards the zero-dimensional gate of the ejecting hemisphere to produce the super-concentration. Wherein, when the pore size of the conducting granule may be roughly 3-5 times or larger the electrolyte concentration-dependent double-layer thickness, the super-concentration may happen. As the concentrated counter-ion is ejected into the electroneutral bulk electrolyte, it attracts co-ions (i.e. particles or molecules having an identical electric property as the conducting granule) and produces a corresponding concentration of the co-ions.
In the present invention, the above-mentioned mechanism is also shown to trap and concentrate co-ion microcolloids which are larger than the nano-pore or nano-channel dimension of the conducting granule. The micro-colloids may be not expected to enter into the conducting granule. However, co-ion micro-colloids can still be attracted to the concentrated counter-ions at the ejecting pole. Bead-based biomolecular assays have attracted considerable attention recently and the possibility of filtering and concentrating such functionalized or hybridized beads on a chip can be quite useful for such assays.
The exemplary embodiments of the present invention will be understood more fully from the detailed description given below and from the accompanying drawings of various embodiments of the invention, which, however, should not be taken to limit the invention to the specific embodiments, but are for explanation and understanding only.
Exemplary embodiments of the present invention are described herein in the context of a method for concentrating particles or molecules and an apparatus thereof.
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We image the enhanced counter-ion concentration not by, for example, counter-ion dye molecules, which may be strongly absorbed to immobilize on the granule prior to entering the nano-pores or nano-channels, but, for example, by fluorescence co-ion dye molecules which may neutralize the counter-ions at the exit of the conducting granule and whose concentration is correspondingly enhanced at that location. An external electric field of about 100 V/cm may be applied on the millimeter-sized conducting granule made of polystyrene resins by a pair of electrodes. The pore size of the conducting granule may be 65 nm, or roughly 3-5 times or larger the double-layer thickness of more concentrated buffer solutions (also as electrolyte solutions) (>0.1 mM). The conducting granule can be either negatively charged (e.g. cation exchange resin granule) or positively charged (e.g. anion exchange resin granule). Fluorescence dye solution of cation (e.g. rhodamine B, rhodanmine110) or anion (e.g. fluorescein, sulforhodamine110) in 10 mM pH buffers is filled in the reservoir prior to the field application. Net charges (mostly counter ions) released from the conducting granule are immediately neutralized by co-ions (i.e. particles or molecules having an identical electric property as the conducting granule) in the bulk in a region close to the conducting granule. Since co-ions as fluorescence dyes are employed to illuminate the phenomenon, an ejection reflects a local increase in the concentration in the neutral bulk close to the conducting granule. The images are digitized and transferred into graphic analysis software, as shown in the
Sequential frames which are taken at 0, 0.36, 0.63, and 0.93 seconds in
By subtracting the blank background (10 mM Tris buffer; pH 8) and correlating the reduced pixel intensity to the dye concentration, the concentration intensity contour in the region highlighted in
To underscore that ion permeation into the conducting granule is necessary for this 106-fold dynamic super-concentration, which was not observed in earlier steady-state experiments with smaller pores, the experiments at various ionic strengths and with a wax bead 71 of similar dimension are carried out. As seen in
A similar co-ion concentration in the bulk region near the ejecting pole is observed when a positively charged granule is used with cationic dye rhodamine B, as shown in the
Similarly when a negatively charged conducting granule is in the reservoir, the trapping of anionic microcolloids tagged with fluorescein dyes is seen. The sequential images in
The above argument corresponds to the counter-ion concentration. However, when the concentrated ions are ejected from the ejecting pole, they attract co-ions to achieve neutrality. In fact, both the co-ion tagged microcolloids and the large co-ion fluorescent dye molecules are probably not the ones being concentrated via transit through the granule and tangential surface flux toward the pole. Rather, it is a smaller counter-ion that is so concentrated with the larger co-ion simply tracking the enhanced counterion concentration as the latter ions exit the double layer into the electroneutral bulk. This is why only the co-ion dye or co-ion dye tagged microcolloids are concentrated by the ion-exchange granules.
Moreover, the present invention further studies the concentration effect of fluorescence dyes (e.g. fluorescein) in different pH Values. Firstly, fluorescein fluorescence dyes with a pKa 6.4˜6.8 are dissolved in 10 mM Tris buffers with pH 6, 6.6 and 8, and the absorption values of these fluorescein solutions with pH 6, 6.6 and 8 are respectively measured by a UV-visible spectroscopy at the detection range of 200-800 nm. Then, the dissociation degrees of these fluorescein solutions in the Tris buffers are calculated by using Beer's law. Additionally, the fluorescein solutions with pH 6, 6.6 and 8 are concentrated with a step change in the field strength 100 V/cm at the ejecting pole of the cation exchange granule. The experimental results, as shown in Table 1, show that the higher the dissociation degree of the fluorescein in the Tris buffer, a concentration effect of the fluorescein is better.
Similarly, the concentration effect of proteins (e.g. fluorescein-tagged bovine-serum albumin (BSA)) in different pH values is studied. Firstly, fluorescein-tagged BSA with a pl 4˜5 are dissolved in 15 mM PBS buffers with pH 5, 6, 6.6, 8 and 8.8. Then, these fluorescein-tagged BSA solutions are concentrated with a step change in the field strength 100 V/cm at the ejecting pole of the cation exchange granule. As shown in Table 2, the experimental results show that the higher the pH value of the fluorescein-tagged BSA in the PBS buffer, a concentration effect of the fluorescein-tagged BSA is better. That is, the higher the pH value, the net charges (negative charges) of the BSA increases. Therefore, the higher the number of charges of the particles in the electrolyte solution, a concentration effect of the particles is better.
While particular embodiments of the present invention have been shown and described, it will be obvious to those skilled in the art that, based upon the teachings herein, changes and modifications may be made without departing from this invention and its broader aspects. Therefore, the appended claims are intended to encompass within their scope of all such changes and modifications as are within the true spirit and scope of the exemplary embodiments of the present invention. In addition, the word “comprising” does not exclude other elements or steps, and the indefinite article “a” or “an” does not exclude a plurality.
This application is a Continuation-In-Part of U.S. patent application Ser. No. 12/383,893, the entire contents of which are incorporated herein by reference.
Number | Date | Country | |
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Parent | 12383893 | Mar 2009 | US |
Child | 12826717 | US |