Sana
Jahanshahi-Anbuhi
a,
Aleah
Henry
a,
Vincent
Leung
a,
Clémence
Sicard
b,
Kevin
Pennings
a,
Robert
Pelton
a,
John D.
Brennan
*b and
Carlos D. M.
Filipe
*a
aDepartment of Chemical Engineering, McMaster University, 1280 Main Street West, Hamilton, ON L8S 4M1, Canada. E-mail: filipec@mcmaster.ca; Fax: +1 905 521 1350; Tel: +1 905 525 9140 (ext. 27278)
bDepartment of Chemistry & Chemical Biology, McMaster University, 1280 Main Street West, Hamilton, ON L8S 4M1, Canada. E-mail: brennanj@mcmaster.ca; Tel: +1 905 525 9140 (ext. 20682)
First published on 4th October 2013
Water soluble pullulan films were formatted into paper-based microfluidic devices, serving as a controlled time shutoff valve. The utility of the valve was demonstrated by a one-step, fully automatic implementation of a complex pesticide assay requiring timed, sequential exposure of an immobilized enzyme layer to separate liquid streams. Pullulan film dissolution and the capillary wicking of aqueous solutions through the device were measured and modeled providing valve design criteria. The films dissolve mainly by surface erosion, meaning the film thickness mainly controls the shutoff time. This method can also provide time-dependent sequential release of reagents without compromising the simplicity and low cost of paper-based devices.
The first prototype of our pesticide sensor was clumsy, labour intensive and required some user skill. The paper sensor strip was first exposed to the test liquid for a fixed time, after which it was dried. In the second step, lateral flow was used to carry the substrate3 to the enzyme layer. In this assay, enzyme deactivation by pesticides in the test liquid and the subsequent generation of color (or lack of it) are time dependent, requiring careful control. On the other hand, the ideal implementation of the pesticide sensor would simply involve dipping one end of a paper strip in the test liquid. After a fixed time the user would then read the color output either qualitatively or possibly more accurately with a scanner or cell phone camera.
Two innovations were required to achieve a more useful format for our pesticide sensor. First we needed a way to sequentially bring two separate liquid streams to the enzyme test zone on the paper sensor. For this, two separate channels were employed – a fast channel that brings test liquid to the enzyme zone first, followed by a slow channel that carried the color producing substrate to the enzyme after a set incubation time.
The second innovation required, and the subject of this paper, was a shutoff valve that stopped the fast channel flow after a fixed time, giving the enzyme zone a chance to dry and accept substrate solution from the slow channel. The fast channel design was described previously and consists of a paper channel sandwiched between hydrophilic films.10 The shutoff valve was a flap valve that needed to be manually actuated. However, this required that a user intervene in the assay at an appropriate time, making the assay less user-friendly and more prone to human error.
Several valve types have been proposed for paper-based microfluidics. Chen et al.11 described a non-return valve (fluidic diode valve), created by strategically patterning hydrophilic regions with and without surfactants, and separating these regions with hydrophobic areas. Fluid flow occurs only from the region containing surfactant (the anode) to the region not containing surfactant. The effect of the surfactant on the surface tension is the driving force directing the flow. This design is capable of forming complex circuits within paper, but it does not function as a shutoff valve. Li et al.12 described a magnetic timing valve using a resistor and an electromagnet that triggers a cantilever valve. However, the incorporation of a resistor and an electromagnet increases the complexity of the device. A number of authors have described timed-opening valves based on filling the paper pores with hydrophobic material13,14,17 such as paraffin wax or with a water-soluble barrier15,16 such as sucrose or trehalose, to provide additional resistance to flow. These temporary barriers delay fluid movement through the channel and allow the user to control the flow rate of the fluid. The flow rate is determined mainly by the barrier thickness, and increasing this factor leads to a reduction in flow rate. While this method of flow control works well for delaying flow, it is insufficient for cases in which different fluids must be delivered to the same space sequentially, as the first sample will not dry and consequently blocks the next fluid from entering the space. Yager and coworkers16 recently reported a barrier composed of sucrose which delays the flow through a paper channel. The timing of the delay is tuneable based on the amount of sucrose that is added. This flow control method allows for sequential reactions, however, the essential flow shut-off system is only provided by a limited sample supply (via source pads). While this is a viable method of metering, it requires more materials to construct each sensor and also increases the possibility of user error, such as an incompletely wetted source pad. A fluid disconnect is yet another type of valve based on the shape of the paper channels. The paper is shaped to have pathways/legs that are sequentially removed from the fluid to stop flow in that channel. These channels allow for multi-step processes, but require specific loading capabilities and cannot be used without a full well of sample.17,18 Although automated sequential delivery has been demonstrated in non-paper-based microfluidic devices,19 we have found very few examples of flow shutoff valves in paper-based devices that do not require electrical power or human intervention.20,21
The essence of our shutoff valve is a pullulan film that dissolves as water flows past it. Pullulan is also the supporting film material used for commercial breath freshening strips; the good film forming properties and rapid dissolution characteristics required for breath strips are also ideal for microfluidic shutoff valves. Pullulan is produced from the fungus Aureobasidium pullulans, and is a non-ionic polysaccharide comprised of three linked maltose residues.22 The molecular weight of pullulan can be as high as 106–107 Da.23 Pullulan is non-hygroscopic, thermally stable and biodegradable.22 In addition, pullulan has good oxygen barrier properties, providing a good encapsulation environment for oxygen sensitive reagents.
The following sections present experiments and models leading to design rules for the pullulan shutoff valves. Finally, we successfully demonstrate the use of the valve to fully automate a previously reported paper-based organophosphate pesticide sensor.3,10
Fig. 1 Schematic of the flow shutoff system assembly. Letters “F” and “R” refer to front and rear side of the device, respectively. |
For ease of cutting, two similarly shaped hole-punchers were made. The smaller hole-punch (~2 mm × 10 mm) was used for cutting the gap in the paper channel, and the larger hole-punch (~3 mm × 10 mm) was used to punch the pullulan films. The main advantage of the hole-punch is its ability to create reproducible and uniform samples. The construction process for the pullulan bridge device demonstrated here is performed at the lab scale. However, the process can be scaled up to produce greater quantities of the device (see the ESI† for a proposed scale-up process).
Fig. 3 shows the relationship between the thickness of the pullulan film and the distance of the liquid flow past the gap. In the pullulan shutoff system, due to the dissolution of the pullulan bridge the upper section of the paper channel is disconnected from the water source; and there is a linear relationship between the thickness of the film and the maximum distance travelled by the liquid. These results are in good agreement with the working principle depicted in Fig. 2. In the ESI† we describe how to cast films with well-defined thicknesses.
We also performed experiments (data not shown) to determine the effect of the widths of the paper channel and pullulan bridge on the behaviour of the device. The effect was found to be negligible, in agreement with the working principle depicted in Fig. 2, where flow switch off is solely dependent on the thickness of the pullulan bridge. No attempts were made to accurately control the size of the gap existing between the pullulan and PET films, since it has been shown by us10 and others27 that the rate at which water moves between two fully wettable flexible surfaces does not depend on the distance between the films at time zero. As the water moves due to capillary action, the films are deformed in response to the capillary force, resulting in the formation of a wedge at the front of the water, i.e. the capillary formed is self-controlled through a balance of capillary forces and the forces associated with the mechanical deformation of the films.
The shutoff system can be divided into three separate sections: the lower section, the bridge section, and the upper section. The lower section starts from the very bottom of the paper strip and ends at the point just before the pullulan film. The bridge section refers to the gap in the channel where a capillary is formed between the PET film and the pullulan film. Finally, the upper section begins at the top edge of the pullulan film and continues to the top of the paper strip.
In the lower section, the water flow in the paper strip is the same as water flow through plain filter paper. This is expected since the lower section is made up of unmodified filter paper. Therefore, the water flow in the lower section follows a modified version of the Lucas–Washburn equation.28
Fig. 4 depicts the experimental data of the water flow on Whatman #1 filter paper strips and shows the comparison between the traditional Lucas–Washburn model and the modified models adapted from N. Fries et al. 200829 and A. Rogacs et al. 2010.30 The two modified models were further altered by taking into account the effect of the water content of the paper fibres.31 Cellulose fibres have a “fibre saturation point” that describes the water content in the pores of the fibre wall. The water in the pores is more difficult to evaporate because of capillary condensation. Due to this, the effect of evaporation cannot be viewed as binary, i.e. the paper is fully dry or the paper is fully wet. Depending on the relative humidity, paper can hold almost 10 w/w% water.32 The models proposed by N. Fries et al. in 200829 assumed the system to be binary, i.e. either wet or dry. This assumption leads to over-prediction of the capillary height rise rate.31 The adjusted model takes into account the water content of the paper fibres and is shown in Fig. 4.
In the full model prediction,29,31 the effects of gravity, evaporation, and water content of the paper fibres have been incorporated into the traditional Lucas–Washburn equation:
(1) |
While in the evaporation model,30,31 the gravitational effect is neglected:
(2) |
Where:
(3) |
From Fig. 4, it can be seen that for paper strips shorter than 10 cm the gravitational effect can be neglected since the deviation of the evaporation model from the full model prediction is less than 0.5%. Thus, the evaporation model was chosen due to its simplicity in comparison to the full model. Furthermore, the evaporation model fits well with the data when the water content of the paper fibre is taken into account.
In the pullulan shutoff system, the water flow in the upper section is much slower than that in the lower section. This is due to the increase in viscosity as the pullulan is dissolved into the solution. Nevertheless, the evaporation model that was applied to the lower section can still be used to describe the flow in the upper section. The main difference between the two sections is the viscosity of the travelling liquid.
To estimate the pullulan concentration in the water after it passes over the pullulan bridge, a series of pullulan solutions of different concentrations were made. The viscosities of these solutions were measured using an Ubbelohde viscometer. The rate of capillary rise of these solutions on Whatman #1 filter paper was measured. As shown in Fig. 5, an increase in concentration leads to slower capillary rise. This is due to the increase in viscosity as the concentration of pullulan increases. Using the viscosities measured for each of the solutions, the evaporation model is fitted to the data. As shown in Fig. 5, the evaporation model adequately describes the data.
Additionally, the rate of water capillary rise through the pullulan shutoff system (Fig. 6) was compared with the results of Fig. 5. It can be seen that the rate of capillary rise for the 50% diluted pullulan solution (20.8 g L−1 pullulan) fits well with the data from water capillary rise through the upper section of the pullulan shutoff system. Therefore, it may be inferred that the solution in the upper section has a similar viscosity to that of the 50% diluted pullulan solution.
Fig. 6 compares rate of capillary rise of the lower and upper sections of the pullulan shutoff device. It also shows the evaporation model for both sections. In the upper section, it should be noted that the deviation which is observed after a specific height (dependent on pullulan film thickness) is due to the full dissolution of the pullulan bridge (refer to Fig. 3) which severs the upper section from the water source.
The pesticide sensor previously reported1,3 is based on the colorimetric detection of acetylcholinesterase (AChE) activity, which is known to be inhibited in the presence of organophosphate pesticides. The sensor exhibits a blue color change in the sensing region in the absence of inhibitors (organophosphate pesticides) in the sample solution, while in the presence of organophosphate pesticides the AChE activity is inhibited, and a dose-dependent decrease in the blue color intensity is observed. The intensity of the color change can be quantitatively analysed, correlating the concentration of pesticide in the sample to the intensity of the color generated.
To detect organophosphate pesticides the sensing (enzyme) zone first needs to be pre-incubated with the sample for at least 2 min prior to the addition of the substrate, as inhibition is time-dependent. The substrate is then introduced to the reaction area after the delay time to elicit a color change. In both of the previous designs the exact moment of when the sensing zone is fully wetted is determined by the user either (a) removing the sensor from the solution in the originally developed bi-directional design (so-called inverted lateral flow),3 or (b) manually switching off the flap valve in the uni-directional design.1 These two previous designs relied on the user's ability to determine the moment when the enzyme zone was fully wetted, which may lead to inconsistent amounts of analyte loaded into the sensing zone and thus irreproducible quantitative results. In order to improve both the reproducibility and ease of use of the sensor, in the present design, the automatic shutoff bridge replaces the manual flap valve as demonstrated in Fig. 7.
Fig. 7 A fully automated bioactive paper sensor for organophosphate pesticide detection. (a) Schematic illustration of the sensor construction (on the left), and an image of the actual device (on the right). The right side of the sensor is covered by PET film to create a ‘fast’ channel.10 An automatic shut-off system (temporary bridge) was created using a soluble pullulan film to control the flow from the covered “fast” channel to the uncovered “slow” channel on the left. A sensing zone (PVAm/SiO2/AChE/SiO2) and a substrate zone (SiO2/IDA/SiO2) were deposited on the uncovered “slow” channel. Following sample introduction, time-sequential schematics are shown as: (b) at around 15 s the sample passes through the “fast” channel and reaches the bridge position; (c) after 2 min the enzyme zone is fully wetted, and due to the dissolution of the soluble pullulan film the bridge automatically disconnects, enabling the sensing zone to dry, and (d) at around 15 min the solution moves through the non-covered “slow” channel and arrives in the pre-wetted enzyme zone and the color change is elicited after 5 min; the intense blue color on the right images was obtained with a Tris buffer solution which did not contain any pesticide, while the left image was obtained for a 10−5 M malathion sample. (e) Plot of dose-dependent inhibition of acetylcholinesterase (AChE) by various concentrations of malathion; three repeats were conducted for each concentration and all points are average of the repeats. |
In this new format, the pullulan temporary bridge-system severs the flow stream from the fast channel automatically and provides a consistent incubation time while allowing the sensing (enzyme) zone to be dried before the substrate arrives. This new format results in a simplified assay that detects the presence of pesticides automatically without any further manipulation from the user.
Fig. 7d illustrates both a positive and a negative test result for the pesticide sensor and Fig. 7e shows a semi logarithmic plot of the dose-dependent inhibition by malathion. As previously reported,3,10 an increasing concentration of malathion progressively inhibits the activity of AChE. The IC50 value for malathion (i.e., 50% inhibition) was 29 nM (calculated by fitting the four parameter Hill equation with SigmaPlot 10.0) and the limit of detection (concentration corresponding to 3 standard deviations below the mean signal from the blank) was 6 nM. The obtained results were comparable with the original sensor. The reliable operation of the pesticide sensor indicates that the functionality of the previously reported sensor3 is not affected by the addition of an automatic flow shut-off system or the presence of the pullulan.
Footnotes |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c3lc50762a |
‡ The film needs to be long enough to slightly overlap the channel, and wider than the gap for gluing purposes. |
This journal is © The Royal Society of Chemistry 2014 |