Abstract
Cryptosporidium, a protozoan pathogen, is a leading threat to public health and the economy. Herein, we report the development of a portable, colorimetric biosensing platform for the sensitive, selective and label/PCR-free detection of Cryptosporidium RNA using oligonucleotides modified gold nanoparticles (AuNPs). A pair of specific thiolated oligonucleotides, complementary to adjacent sequences on Cryptosporidium RNA, were attached to AuNPs. The need for expensive laboratory-based equipment was eliminated by performing the colorimetric assay on a micro-fabricated chip in a 3D-printed holder assembly. A smartphone camera was used to capture an image of the color change for quantitative analysis. The detection was based on the aggregation of the gold nanoparticles due to the hybridization between the complementary Cryptosporidium RNA and the oligonucleotides immobilized on the AuNPs surface. In the complementary RNA’s presence, a distinctive color change of the AuNPs (from red to blue) was observed by the naked eye. However, in the presence of non-complementary RNA, no color change was observed. The sensing platform showed wide linear responses between 5 and 100 µM with a low detection limit of 5 µM of Cryptosporidium RNA. Additionally, the sensor developed here can provide information about different Cryptosporidium species present in water resources. This cost-effective, easy-to-use, portable and smartphone integrated on-chip colorimetric biosensor has great potential to be used for real-time and portable POC pathogen monitoring and molecular diagnostics.
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Introduction
Cryptosporidium spp. is a major intestinal protozoan pathogen in adults, children and numerous animal species worldwide. Recently, cryptosporidiosis, an infection caused by Cryptosporidium, has become a global threat to public health and the economy1. Moreover, Cryptosporidium contamination has increased the challenge to deliver safe drinking water in developing and developed countries2,3,4. The pathogen can cause death in children and immuno-compromised individuals and severe cryptosporidiosis in healthy adults5,6.
Several techniques have been used to detect Cryptosporidium oocysts in water samples, including fluorescence microscopy-based methods (e.g. Environmental Protection Agency (EPA) 1623)7, immunoassays8,9 and molecular techniques10,11. These methods are time-consuming, insufficient, expensive and require well-trained personnel. In particular, immunological and molecular techniques require extensive sample preparation, including labelling with expensive fluorescence labels, amplification and sophisticated lab-based equipment for detection and data analysis12. These challenges make this method unsuitable for on-site detection and the fast-decision-making process13,14. Therefore, it is necessary to develop a simple, user-friendly, rapid, cost-effective, label/PCR-free and sensitive method for on-site detection of Cryptosporidium in water samples.
Recently, colorimetric detection based on inorganic nanomaterials has attracted great attention due to their simplicity, cost-effectiveness, and distinct color variation associated with their morphology or size change15,16,17. Moreover, colorimetric assays can be visualized with the naked eye without the need for sophisticated instruments or tedious training18. Gold nanoparticles (AuNP) colorimetric assays are of particular interest because of their unique features, including their catalytic properties and controllable sizes19. More importantly, they are easily synthesizable and modified with several thiolated molecular recognition elements20. Furthermore, the unique localized surface plasmon resonance (LSPR) properties of AuNPs allow them to have different colors based on their size21. For example, AuNPs with 20 nm have a red color, and their LSPR can be measured at a wavelength of 520 nm21,22. Colloidal AuNPs are negatively charged and hence repel each other. The repulsion between the particles allows them to stay colloidal and maintain their red color. However, when salt such as NaCl is added, these negative charges are neutralized (masked), resulting in the aggregation of AuNPs. Aggregation results in a decrease in the distance between the particles and an increase in their size. This results in a change in color from red to blue due to a large shift of the LSPR peak (absorption at a longer wavelength)23.
In DNA biosensing, gold nanoparticles are usually modified with a biological recognition element such as a complementary oligonucleotide specific and selective to the target DNA or RNA. The hybridization between the modified AuNPs and the target DNA or RNA in the sample results in a change in color from red to blue. The color change is proportional to the analyte concentration in the sample and can be qualitatively detected by the naked eyes24. Due to these features, AuNPs have led to a new generation of biosensors with high stability, selectivity and sensitivity.
Recently, portability has become an increasingly important goal for developing sensing platforms for many applications25. On-chip biosensors are one of the most exploited techniques used to produce cost-effective and portable miniaturized sensing platforms26. A typical on-chip-based biosensor consists of a recognition element (such as antibodies27, nucleic acids28, enzymes29,30, aptamers31 or whole cells32), transducer, and detector33. The recognition element dictates the biosensing platform specificity and selectivity34, while the transducer transforms the response produced from a biorecognition event to a measurable signal35. These platforms can be advantageous in a wide range of applications, including food safety36, diagnostics37, security and defense38,39, and environmental monitoring40. This is due to their cost-effectiveness, disposability, simplicity, low power requirements and sample-reagent usage40. However, most colorimetric detection methods still need advanced and expensive equipment to read and analyze the results41,42. Therefore, the applicability of using these techniques for on-site detection and point-of-care (POC) is still limited43,44.
In the last decade, smartphones with internal memory storage, touchscreen displays, internet connectivity (enabling data exchange wirelessly over the internet), advanced compute power, and high-resolution cameras have gained significant market acceptance for POC applications45. Given the iniquitousness of smartphone access, smartphone-integrated biosensing platforms can serve as a accessible and low-cost solutions for routine (daily) testing without requiring highly-trained personnel and bulky, expensive and complicated laboratory instrumentations such as spectrophotometers and microscopes, especially in resource-limited countries and rural areas46,47. As an example, Breslauer et al.48 developed a mobile phone-mounted light microscope with 350×magnification and demonstrated its potential for global health applications. Smartphone-based image capture and analysis systems have also been applied for monitoring immunoassays such as colorimetric and fluorescence assays49,50, DNA diagnostics51, label-free detection of pathogens52, quantum-dots labelling53,54 and fluorescence microscopy54,55. Smartphones have also been used as a spectrophotometer with a wavelength resolution of 5 nm56. These advantages have led to increasing research and industrial interest in using smartphones to detect analytes of environmental57,58,59, food safety60,61, personal health62, and biomedical50,54,63,64 applications. This has led to integrating smartphones as smart detectors, signal inducers, and data processors with the on-chip-based biosensing technology for rapid, cost-effective, easy-to-use, real-time and POC diagnostics65,66,67,68. An additional attachment or cradle is used with these integrations to mount the smartphone and other components69,70,71,72. These integrated systems have allowed many analyses to be performed remotely outside the laboratory (at the point of need)56,73,74.
This research describes the development of a simple, cost-effective, easy to fabricate, sensitive and portable on-chip-based colorimetric biosensor for the direct and label/PCR-free detection of Cryptosporidium RNA. Compared to DNA, RNA is shorter and allows for the direct detection of a single mismatch or mutation without amplification (PCR). Hence, RNA was used as the target analyte in this project75. The colorimetric sensing mechanism is based on two sets of modified AuNPs with specific oligonucleotides complementary to adjacent sequences on Cryptosporidium RNA. Upon adding Cryptosporidium RNA into the modified AuNPs solution, hybridization between two complementary sets of oligonucleotides immobilized on the AuNPs and the RNA occurs, forming a network of oligonucleotide-AuNPs. The aggregation of AuNPs results in a colorimetric shift due to the change in LSPR due to a reduction in the distance between the AuNPs and hence an increase in the size of the AuNPs. The outcome is a visible color change of the AuNPs from red to blue, observed and recorded within 5 min (Fig. 1). The colorimetric assay was performed on a fabricated chip integrated with a 3D-printed holder assembly to facilitate its applicability for on-site detection and POC applications. A smartphone in a 3D-printed holder assembly was used to measure the color change due to the target analyte's presence (Cryptosporidium RNA). A smartphone was chosen based on its lightweight, portability, on-site image analysis, and data transmission capability. All these advantages are suitable for in-field detection and POC applications. The sensing platform in this research has provided an exclusive sensitivity, selectivity and portability towards the detection of Cryptosporidium RNA: a 5 µM of Cryptosporidium RNA spiked in water samples can be detected via the developed on-chip colorimetric assay in 30 min, reducing the turnaround detection time following RNA extraction from contaminated sites. The results generated by the developed sensing platform were in good agreement with those generated by the conventional spectroscopic techniques. All these confirm the developed sensing platform combined with the 3D-printed holder assembly integrated with a smartphone could directly detect different Cryptosporidium RNA concentrations in a spiked sample without DNA amplification. Furthermore, the on-chip sensing platform developed in this research showed the sensor's capability to detect Cryptosporidium and distinguish between its different species. This capability is crucial to allow appropriate risk assessments.
Materials
Gold nanoparticles (AuNPs) with a diameter of 20 nm were purchased from Cytodiagnostics (Canada). According to the manufacturer, AuNPs were synthesized by citrate reduction, and thus they have negatively charged citrate ions adsorbed on their surface, which enhance their stabilization via electrostatic repulsion. Two sets of thiolated-oligonucleotides capturing probes and Cryptosporidium RNA were designed and purchased from Integrated DNA Technologies (IDT, Canada) (Table 1). Sodium phosphate monobasic monohydrate, sodium phosphate dibasic, DL-Dithiothreitol (DTT), sodium azide (NaN3), dextran sulfate, formamide, sodium chloride and sodium dodecyl sulfate were purchased from Sigma-Aldrich (Canada). Illustra NAP 5 columns were purchased from VWR (Canada). All other reagents and solvents were of the analytical grade and purchased from Sigma Aldrich. Ultrapure water was used throughout the experiments.
Instruments
All ultraviolet–visible (UV–vis) spectral measurements were carried out by double beam spectrophotometer, Cary 3500 UV–vis. A 1-cm path length quartz cuvettes were used for all measurements. An Oakton pH meter (Oakton Instruments, pH 510 series) was calibrated against three standard buffer solutions with three different pH values (4.0, 7.0 and 10) and used for the pH determination.
Experimental methods
Sensor fabrication
The fabrication of the chip-based colorimetric biosensor was performed as previously described in76. All glass slides were cleaned by using piranha solution followed by an oxygen plasma treatment for 10 min. Chromium and gold layers with thicknesses of 50 nm and 250 nm, respectively, were sputtered (Angstrom Engineering) on the cleaned glass slides in an argon atmosphere. Sensing transparent circular zones with a diameter of 3 mm were patterned using the standard lithography process, as described in3. A lift-off procedure was followed to create hydrophobic circular barriers around the detection zone. This process has led to circular hydrophobic barriers around the detection spot to control the sample in the sensing area.
Holder assembly fabrication
The 3D portable holder assembly integrated with a smartphone is shown in Fig. 2. A smartphone camera is used to collect image samples. An open-source application (Color Grab, Loomatix) from the android store is used to analyze the collected images and display the analyte concentration to the user. A battery built in the smartphone is used to supply power. This allows the smartphone to be charged using an inexpensive micro-USB connector, enabling the smartphone to operate on the battery power for several hours43. The smartphone touch screen is used to control the detection process. Furthermore, the smartphone's built-in Wi-Fi chip allows a 2.4 GHz wireless network to transfer data for further analysis on an external computer or external storage when required. A three-dimensional-printed holder assembly was designed and fabricated to house all the chips and the smartphone inside a compact unit.
Conjugation of thiolated oligonucleotide to gold nanoparticles
The conjugation of the two sets of thiolated oligonucleotides (Table 1) to gold nanoparticles was carried out via two parts involving: (1) the reduction of the two sets of thiolated oligonucleotides, and (2) the conjugation of the reduced oligonucleotides to the gold nanoparticles. In the first part, the two sets of lyophilized oligonucleotides were dissolved to a final concentration of 500 µM in ultrapure water. A 50 µL dissolved oligonucleotide was then mixed with 450 µL of 0.15 M sodium phosphate buffer supplemented with 0.1 M DTT. Following this step, the mixture was incubated at room temperature for 2 h to reduce the oligonucleotides. Subsequently, A NAP 5 column operated in water was used to separate the reduced oligonucleotides from trityl-SH and DTT. The final elute from the NAP 5 column was 1 mL in water with an approximate concentration of 25 μM. The final concentration of the elute was measured with UV–vis spectroscopy by measuring the absorbance at 260 nm.
A 1 mL solution of unmodified gold nanoparticles was transferred to a 1.5 mL Eppendorf tube in the second part. Then, 24 µL of the reduced thiolated oligonucleotides (25 μM in water, equivalent to 0.025 nmol/μL) was added to the gold nanoparticles and incubated for 1 h at room temperature. Following this step, 0.1 M sodium phosphate buffer (pH 7.0) was added to the mixture in a stepwise manner (in 10 μL increment with 5 min incubation time in between) until a final concentration of 10 mM sodium phosphate (pH 7.0) was achieved. Subsequently, 1 M NaCl was added in a similar stepwise manner until a final concentration of 100 mM was reached. The mixture was then incubated at 4 °C for 16 h. The above steps minimize the aggregation of the gold nanoparticles by immobilizing the thiolated oligonucleotides properly onto the gold nanoparticles' surface, which improves the overall stability and quality of the conjugation process. The conjugated gold nanoparticles were then centrifuged at 17,000×g for 30 min to pellet the oligonucleotide gold conjugate. Lastly, the supernatant was removed, and the oligonucleotide gold conjugate was resuspended in 200 μL of 10 mM sodium phosphate buffer, 100 mM NaCl and 0.01% (w/v) NaN3.
Sample preparation and colorimetric measurements of Cryptosporidium RNA
For the colorimetric detection of Cryptosporidium RNA using the developed sensing platform, 3 µL of AuNPs modified with probe A (25 μM), and 3 µL of AuNPs modified with probe B (25 μM) were first added to the sensing zone on the fabricated chip. Next, 5 µL of different concentrations of Cryptosporidium RNA (5, 25, 60, 100, 200 and 300 µM) and 4 µL of hybridization buffer (a stock solution of 16% dextran sulfate and 20% formamide) were added to the modified AuNPs. The chip was then incubated at 70 °C for 15 min, followed by incubation at 37 °C for 20 min. Lastly, the chip was inserted in the holder assembly at room temperature. The presence of Cryptosporidium RNA in the sample results in a detectable color change after 5 min in the detection zone patterned on a chip, which can be visualized by the naked eye.
For quantitative analysis, the color change is captured by a smartphone camera (Samsung Galaxy Note 10) integrated with a 3D-printed holder assembly under controlled light conditions. A region of interest (ROI) in the captured image was selected and fixed for consistency measurements. An open-source application (Color Grab, Loomatix) from the android application store was installed on the smartphone and used for converting the ROI from the red, green, blue (RGB) color space to the Hue, Saturation, Value (HSV) color space. This previous step was performed to achieve a linear relationship between the color components and the color change. Image analysis was performed by calculating the Saturation value of the recorded images' HSV coordinates and correlated to the sample's analyte concentration.
For the UV–vis measurements, the same concentrations were used in a 1 mL volume sample. All measurements were performed before and after the incubation with different Cryptosporidium RNA concentrations and were repeated three times to confirm the detection limit and conduct a statistical error analysis.
Calibration curve, limit of detection (LOD), and selectivity
To assess the developed on-chip colorimetric sensor's applicability, a calibration curve was obtained by plotting A630/A523 nm absorption ratio and Saturation values of the HSV coordinates of the recorded images versus the RNA concentration using the UV–vis and the smartphone, respectively. The limit of detection (LOD) was calculated using the following expression: LOD = 3SDb/m, where SDb is the standard deviation of the blank and m is the slope of the calibration curve77,78.
To evaluate the developed sensing platform's selectivity, aqueous solutions spiked with a non-complementary RNA consisting of 42 nucleotides (random sequence RNA) were tested and used as the control (see Table 1).
Results and discussion
Evaluation of AuNPs conjugation using UV–visible spectroscopy
To confirm the conjugation of AuNPs with the oligonucleotides, UV–vis spectra were recorded for AuNPs colloid (20 nm) before and after conjugation (Fig. 3). Gold nanoparticles colloid (with a diameter of 20 nm) exhibits an extinction maximum at wavelength 520 (Fig. 3). After conjugating the AuNPs with oligonucleotides, a slight shift of 3 nm in the absorption wavelength was observed. This slight shift confirms the conjugation of AuNPs.
Detection of Cryptosporidium RNA using UV–vis spectroscopy
The colorimetric assay was first tested with different Cryptosporidium RNA concentrations, as described in “Sample preparation and colorimetric measurements of Cryptosporidium RNA” section, and verified using UV–vis spectroscopy. The UV–vis spectroscopy results in Fig. 4a) show that the presence of different analyte concentrations in the sample results in a decrease in the absorption peak at 523 nm, while there is a gradual increase in the absorption peak of 630 nm. Hence, the A630/A523 ratio was used in this study to investigate the aggregation state of the modified AuNPs. Figure 4b) shows that increasing the target analyte's concentration from 5 µM to 300 µM has led to a gradual increase in the A630/A523 ratio, and a noticeable color change of AuNPs from red to blue was observed.
Furthermore, the color change can be visualized at high concentrations of the target analyte (> 25 µM) (see the inset in Fig. 4a)). The A630/A523 ratio plotted versus the RNA concentration in the sample exhibited an excellent linear range between 5 µM and 100 µM with a detection limit of approximately 5 µM. The detection limit (calculated as described in “Calibration curve, limit of detection (LOD), and selectivity” section) was determined from the calibration curve created by plotting the 630/523 nm absorption ratio, demonstrating the degree of AuNPs aggregation versus the analyte concentration. Although the apparent detection limit visualized by the naked eye was 25 µM (see the inset in Fig. 4a)), quantitative analysis needs to be performed relative to the blank color. Otherwise, misanalysing under different environmental conditions can occur.
Detection of Cryptosporidium RNA using on-chip biosensor
The sensor response from different concentrations of Cryptosporidium RNA is presented in Fig. 5. The colorimetric results show that increasing the analyte concentration from 5 µM to 300 µM results in a decrease in the Saturation value (S) of the HSV coordinates of the recorded images and a distinct color change (see the inset in Fig. 5a)). We found that the S value is more reliable and accurate than the H and V values for monitoring the sample's RNA concentration. The sensor showed a wide linear response between 5 µM and 100 µM with a detection limit of approximately 5 µM (see Fig. 5b)). The results obtained by the developed sensing platform show a good agreement with the results obtained by the conventional method (UV–vis spectroscopy). However, the sensing platform results are more easily differentiable (see the inset in Fig. 5a)).
Additionally, the sample volume used with the on-chip method was 15 µL, making the proposed sensing platform safer and less expensive than the UV–vis spectroscopy that requires a larger sample volume (e.g., 1 mL). Furthermore, small volumes result in a shorter analysis time so that the total analysis time can be reduced from hours to 30 min. Moreover, multiple samples from different contaminated sites can be analyzed at once, which will further shorten the analysis time and result in a large-scale screening process.
The detection limit achieved was high (5 µM) compared to those reported in79. However, unlike our sensing platform, in79, DNA amplification was conducted to enhance the sensitivity. This has resulted in increasing the cost, analysis time and hindered portability and thus on-site detection. In our sensing platform, DNA oligonucleotides were used and the capture probe for the detection of RNA. This has increased the number of base-pairs mismatch between DNA and RNA and thus incomplete hybridization, which results in less sensitivity and detection limit. The use of RNA oligoprobes (capture probe) is expected to enhance the detection limit and sensitivity by 10 orders of magnitude. This is due to the high degree of stability of RNA/RNA hybrid duplexes compared to RNA/DNA ones80.
Selectivity of colorimetric assay towards Cryptosporidium RNA
To investigate the selectivity of the developed colorimetric assay, the degree of the color change of the modified AuNPs towards the analyte of interest and a non-complementary sequence RNA consists of 42 nucleotides (random sequence RNA) were recorded by both UV–vis spectroscopy (Fig. 6a)) and the developed sensing platform (Fig. 6b)). In this experiment, the concertation of the target analyte and the random sequence was 200 µM. A high concentration of Cryptosporidium RNA and the random sequence RNA was chosen to investigate the effect of other random bacterial sequences RNA in high-contaminated samples. The results show that a high concentration of a random sequence RNA does not induce any noticeable color change (minor changes of A630/A523 ratio in Fig. 6a)) to the modified AuNPs. In contrast, with the addition of 200 µM of Cryptosporidium RNA, a significant increase of A630/A523 was observed. In the case of the developed sensing platform (see Fig. 6b)), a considerable decrease in the S value from 175 (random sequence RNA, which approximately equals to the S value of the blank) to 53 (Cryptosporidium RNA). The results confirm the high selectivity of the developed colorimetric assay and the sensing platform to detect Cryptosporidium RNA in complex samples.
Data validation
Additional experiments were performed to investigate the repeatability, practicality, accuracy and reliability of the developed sensing platform. Five samples with different concentrations (5, 10, 15, 20 and 25 µM) were prepared as described in “Sample preparation and colorimetric measurements of Cryptosporidium RNA” section. All measurements were performed under the same conditions as those performed for the calibration measurements. Table 2 summarizes a comparison between the prepared sample concentrations and those obtained by the developed sensing platform.
In general, the obtained results are in good agreement, with maximum errors occurring at the lowest concentration (5 µM).
Table 3 shows a comparison of methods reported in the literature to date for the detection of Cryptosporidium with the developed sensing platform in terms of detection principle, advantages, and disadvantages.
Conclusions
A simple and cost-effective colorimetric assay combining the chemical and photoelectric properties of AuNPs on a chip with 3D-printed holder assembly integrated with a smartphone was developed for the sensitive, label-free and on-site detection of Cryptosporidium specific RNA. This sensing platform eliminated the need for PCR amplification, well-trained personnel and bulky instruments. Two sets of AuNPs modified with oligonucleotides capturing probes specific and complementary to adjacent sequences on Cryptosporidium rRNA were used to enhance the specificity and selectivity towards the analyte of interest to reduce the inference from undesired substances in the sample. After assessing the colorimetric assay using UV–vis spectroscopy, the assay was tested using the developed sensing platform to confirm the applicability, reproducibility and reliability of the sensing platform for the quantitative detection of Cryptosporidium.
Under optimized conditions, results obtained from the UV–vis spectroscopy and the developed sensing platform showed a linear detection range between 5 and 100 µM with a detection limit of 5 µM. The detection limit obtained by the developed sensing platform was similar to the detection limit obtained by UV–vis spectroscopy without using bulky and advanced laboratory equipment. The total turnaround analysis time using the developed sensing platform was reduced from hours to 30 min. Even when a high concentration of random sequences RNA in spiked samples were tested with the developed sensing assay, the developed sensing platform showed high selectivity and specificity towards Cryptosporidium RNA. Furthermore, the sample volume used for measurements using the developed sensing platform was 15 µL, which reduces the sample volume and cost required for a single measurement required for analysis compared to the conventional method. In addition to the direct measurement of Cryptosporidium RNA without amplification, this sensing platform enables a simple way to screen multiple samples for Cryptosporidium from different contaminated sites and quantitatively determine the concentration of Cryptosporidium in the sample.
This smartphone-integrated sensing platform is a steppingstone towards creating ubiquitous and accessible pathogen detection technologies that could potentially be used in resource-limited settings, however, there are some outstanding challenges that need to be met before a field-ready technology is accomplished. One limitation of this technology is that it suffers from limited environmental control when used in open environments where ambient light or vibrations can negatively impact the sensing performance. Overcoming this challenge requires constructing the 3D attachment or enclosure with all the necessary hardware to perform measurements and then connect the attachment through Bluetooth or wire to the smartphone. This will reduce the interference from ambient light and vibrations and enable better control and stability of the attachment. Another challenge is lowering the detection limit below 5 µM of Cryptosporidium RNA. The developed sensing platform shows maximum errors at low RNA concentrations. Future research efforts are required to characterize the effect of AuNPs size and RNA-induced aggregation in order to enhance the detection limit. Future studies are also required to study the replacement of the DNA oligonucleotides with RNA oligoprobes to increase the degree of stability of RNA/RNA hybrid duplexes compared to the RNA/DNA ones80 as well as testing the sensor with other potential interferants. Multidisciplinary research efforts are required to design and test real-time and high-throughput systems for detecting Cryptosporidium spp. in the water supply chains with high sensitivity and reproducibility in order to harmonize global efforts to monitor and prevent waterborne infectious diseases using such technologies.
References
Iqbal, A. et al. Detection of Cryptosporidium parvum oocysts on fresh produce using DNA aptamers. PLoS ONE 10, 1–13 (2015).
Luka, G. et al. Label-free capacitive biosensor for detection of Cryptosporidium. Sens. (Basel). 19, 258 (2019).
Samiei, E., Luka, G. S., Najjaran, H. & Hoorfar, M. Integration of biosensors into digital microfluidics: Impact of hydrophilic surface of biosensors on droplet manipulation. Biosens. Bioelectron. 81, 480–486 (2016).
Luka, G. et al. Comprehensive review of conventional and state-of-the-art detection methods of Cryptosporidium. J. Hazard. Mater. 421, 126714 (2022).
Bridle, H. et al. Detection of Cryptosporidium in miniaturised fluidic devices. Water Res. 46, 1641–1661 (2012).
Tzipori, S. & Widmer, G. A hundred-year retrospective on cryptosporidiosis. Trends Parasitol. 24, 184–189 (2008).
U.S. Environmental Protection Agency. USEPA method 1622: Cryptosporidium in water by filtration/IMS/IFA. EPA 821-R-98-010. in (Office of Water, U.S. Environmental Protection Agency, 1998).
Jayalakshmi, J., Appalaraju, B. & Mahadevan, K. Evaluation of an enzyme-linked immunoassay for the detection of Cryptosporidium antigen in fecal specimens of HIV/AIDS patients. Indian J. Pathol. Microbiol. 51, 137–138 (2008).
Cunha, F. S., Peralta, R. H. S. & Peralta, J. M. New insights into the detection and molecular characterization of Cryptosporidium with emphasis in Brazilian studies: A review. Rev. Inst. Med. Trop. Sao Paulo 61, 1–12 (2019).
Brescia, C. C. et al. Cryptosporidium propidium monoazide-PCR, a molecular biology-based technique for genotyping of viable Cryptosporidium oocysts. Appl. Environ. Microbiol. 75, 6856–6863 (2009).
U.S. Environmental Protection Agency. Method 1623: Cryptosporidium and Giardia in water by filtration, immunomagnetic separation, and fluorescent antibody. (Office of Water, 2001). Publication EPA-821-R-01-025.
Cheun, H. I. et al. Development of a Diagnostic Kit to Detect Cryptosporidium parvum and Giardia lamblia. Osong Public Heal. Res. Perspect. 4, 146–151 (2013).
Roellig, D. M. et al. Community laboratory testing for Cryptosporidium: Multicenter study retesting public health surveillance stool samples positive for Cryptosporidium by rapid cartridge assay with direct fluorescent antibody testing. PLoS ONE 12, 1–13 (2017).
Robinson, T. J., Cebelinski, E. A., Taylor, C. & Smith, K. E. Evaluation of the positive predictive value of rapid assays used by clinical laboratories in Minnesota for the diagnosis of cryptosporidiosis. Clin. Infect. Dis. 50, e53–e55 (2010).
Xia, F. et al. Colorimetric detection of DNA, small molecules, proteins, and ions using unmodified gold nanoparticles and conjugated polyelectrolytes. Proc. Natl. Acad. Sci. 107, 10837–10841 (2010).
Jazayeri, M. H., Aghaie, T., Avan, A., Vatankhah, A. & Ghaffari, M. R. S. Colorimetric detection based on gold nano particles (GNPs): An easy, fast, inexpensive, low-cost and short time method in detection of analytes (protein, DNA, and ion). Sens. Bio-Sens. Res. 20, 1–8 (2018).
Liu, L., Hao, Y., Deng, D. & Xia, N. Nanomaterials-based colorimetric immunoassays. Nanomater (Basel, Switzerland) 9, 316 (2019).
Wachiralurpan, S. et al. Rapid colorimetric assay for detection of Listeria monocytogenes in food samples using LAMP formation of DNA Concatemers and gold nanoparticle-DNA probe complex. Front. Chem. 6, 90 (2018).
Daniel, M.-C. & Astruc, D. Gold nanoparticles: Assembly, supramolecular chemistry, quantum-size-related properties, and applications toward biology, catalysis, and nanotechnology. Chem. Rev. 104, 293–346 (2004).
Spampinato, V., Parracino, M. A., La Spina, R., Rossi, F. & Ceccone, G. Surface analysis of gold nanoparticles functionalized with thiol-modified glucose SAMs for biosensor applications. Front. Chem. 4, 8 (2016).
Fong, K. E. & Yung, L.-Y.L. Localized surface plasmon resonance: A unique property of plasmonic nanoparticles for nucleic acid detection. Nanoscale 5, 12043–12071 (2013).
Zuber, A. et al. Detection of gold nanoparticles with different sizes using absorption and fluorescence based method. Sens. Actuators B Chem. 227, 117–127 (2016).
Pluchery, O., Remita, H. & Schaming, D. Demonstrative experiments about gold nanoparticles and nanofilms: An introduction to nanoscience. Gold Bull. 46, 319–327 (2013).
Franco, R., Pedrosa, P., Carlos, F. F., Veigas, B. & Baptista, P. V. Gold nanoparticles for DNA/RNA-based diagnostics. Handb. Nanoparticles https://doi.org/10.1007/978-3-319-15338-4_31 (2015).
Yeo, J. C. & Lim, C. T. Emerging flexible and wearable physical sensing platforms for healthcare and biomedical applications. Microsystems Nanoeng. 2, 16043 (2016).
Mejía-Salazar, J. R., Cruz, K. R., Vásques, E. M. M. & de Oliveira, O. N. Microfluidic point-of-care devices: New trends and future prospects for ehealth diagnostics. Sens. (Switzerland) 20, 1–19 (2020).
Xiang, C. et al. Sensitive electrochemical detection of Salmonella with chitosan-gold nanoparticles composite film. Talanta 140, 122–127 (2015).
Hassan, R. A., Heng, L. Y. & Tan, L. L. Novel DNA biosensor for direct determination of Carrageenan. Sci. Rep. 9, 6379 (2019).
Yang, H. Enzyme-based ultrasensitive electrochemical biosensors. Curr. Opin. Chem. Biol. 16, 422–428 (2012).
Fordwour, O. B., Luka, G., Hoorfar, M. & Wolthers, K. R. Kinetic characterization of acetone monooxygenase from Gordonia sp. strain TY-5. AMB Express 8, 181 (2018).
Contreras Jiménez, G. et al. Aptamer-based label-free impedimetric biosensor for detection of progesterone. Anal. Chem. 87, 1075–1082 (2015).
May, K. M. L., Wang, Y., Bachas, L. G. & Anderson, K. W. Development of a whole-cell-based biosensor for detecting histamine as a model toxin. Anal. Chem. 76, 4156–4161 (2004).
Mohanty, S. P. & Kougianos, E. Biosensors: A tutorial review. IEEE Potent. 25, 35–40 (2006).
Long, F., Zhu, A. & Shi, H. Recent advances in optical biosensors for environmental monitoring and early warning. Sens. (Basel). 13, 13928–13948 (2013).
Wu, J., Fu, Z., Yan, F. & Ju, H. Biomedical and clinical applications of immunoassays and immunosensors for tumor markers. TrAC Trends Anal. Chem. 26, 679–688 (2007).
Yoon, J.-Y. & Kim, B. Lab-on-a-chip pathogen sensors for food safety. Sens. (Basel). 12, 10713–10741 (2012).
Wu, J., Dong, M., Rigatto, C., Liu, Y. & Lin, F. Lab-on-chip technology for chronic disease diagnosis. npj Digit. Med. 1, 7 (2018).
Luka, G. et al. Microfluidics integrated biosensors: A leading technology towards lab-on-a-chip and sensing applications. Sensors 15, 30011–30031 (2015).
Luka, G., Ahmad, S., Falcone, N., Kraatz, H.-B. & Kraatz, B. Advances in enzyme-based electrochemical sensors: current trends, benefits, and constraints. In Bioelectronics and Medical Devices (eds. Pal, K. et al.) 555–590 (Woodhead Publishing, 2019). https://doi.org/10.1016/B978-0-08-102420-1.00029-7.
Dhar, B. C. & Lee, N. Y. Lab-on-a-chip technology for environmental monitoring of microorganisms. BioChip J. 12, 173–183 (2018).
Morbioli, G. G., Mazzu-Nascimento, T., Stockton, A. M. & Carrilho, E. Technical aspects and challenges of colorimetric detection with microfluidic paper-based analytical devices (μPADs): A review. Anal. Chim. Acta 970, 1–22 (2017).
Alberti, G., Zanoni, C., Magnaghi, L. R. & Biesuz, R. Disposable and low-cost colorimetric sensors for environmental analysis. Int. J. Environ. Res. Public Health 17, 1–23 (2020).
Luka, G. S., Nowak, E., Kawchuk, J., Hoorfar, M. & Najjaran, H. Portable device for the detection of colorimetric assays. R. Soc. Open Sci. 4, 171025 (2017).
Luka, G. S., Nowak, E., Kawchuk, J., Hoorfar, M. & Najjaran, H. Data from: Portable device for the detection of colorimetric assays. https://doi.org/10.5683/SP2/N30PGD.
Vashist, S. K., Mudanyali, O., Schneider, E. M., Zengerle, R. & Ozcan, A. Cellphone-based devices for bioanalytical sciences. Anal. Bioanal. Chem. 406, 3263–3277 (2014).
Erickson, D. et al. Smartphone technology can be transformative to the deployment of lab-on-chip diagnostics. Lab Chip 14, 3159–3164 (2014).
Geng, Z. et al. Recent progress in optical biosensors based on smartphone platforms. Sens. (Basel). 17, 2449 (2017).
Breslauer, D. N., Maamari, R. N., Switz, N. A., Lam, W. A. & Fletcher, D. A. Mobile phone based clinical microscopy for global health applications. PLoS ONE 4, e6320 (2009).
Mudanyali, O. et al. Integrated rapid-diagnostic-test reader platform on a cellphone. Lab Chip 12, 2678 (2012).
Cai, G., Yu, Z., Tong, P. & Tang, D. Ti3C2 MXene quantum dot-encapsulated liposomes for photothermal immunoassays using a portable near-infrared imaging camera on a smartphone. Nanoscale 11, 15659–15667 (2019).
Guo, X. et al. Smartphone-based DNA diagnostics for malaria detection using deep learning for local decision support and blockchain technology for security. Nat. Electron. 4, 615–624 (2021).
Dönmez, S. İ, Needs, S. H., Osborn, H. M. I. & Edwards, A. D. Label-free smartphone quantitation of bacteria by darkfield imaging of light scattering in fluoropolymer micro capillary film allows portable detection of bacteriophage lysis. Sens. Actuators B Chem. 323, 128645 (2020).
Zhu, H., Sikora, U. & Ozcan, A. Quantum dot enabled detection of Escherichia coli using a cell-phone. Analyst 137, 2541–2544 (2012).
Qiu, Z., Shu, J. & Tang, D. Bioresponsive release system for visual fluorescence detection of Carcinoembryonic antigen from Mesoporous silica nanocontainers mediated optical color on quantum dot-enzyme-impregnated paper. Anal. Chem. 89, 5152–5160 (2017).
Wei, Q. et al. Fluorescent imaging of single nanoparticles and viruses on a smart phone. ACS Nano 7, 9147–9155 (2013).
Smith, Z. J. et al. Cell-phone-based platform for biomedical device development and education applications. PLoS ONE 6, e17150 (2011).
Shu, J., Qiu, Z. & Tang, D. Self-referenced smartphone imaging for visual screening of H2S Using CuxO-polypyrrole conductive aerogel doped with graphene oxide framework. Anal. Chem. 90, 9691–9694 (2018).
Nguyen, V. K., Renault, É. & Milocco, R. Environment monitoring for anomaly detection system using smartphones. Sensors 19, 3834 (2019).
Andrachuk, M., Marschke, M., Hings, C. & Armitage, D. Smartphone technologies supporting community-based environmental monitoring and implementation: A systematic scoping review. Biol. Conserv. 237, 430–442 (2019).
Yu, L. et al. Disposable lateral flow-through strip for smartphone-camera to quantitatively detect alkaline phosphatase activity in milk. Biosens. Bioelectron. 69, 307–315 (2015).
Li, Z. et al. Smartphone-based visualized microarray detection for multiplexed harmful substances in milk. Biosens. Bioelectron. 87, 874–880 (2017).
Zeng, R. et al. CRISPR-Cas12a-driven MXene-PEDOT:PSS piezoresistive wireless biosensor. Nano Energy 82, 105711 (2021).
Lee, D., Chou, W. P., Yeh, S. H., Chen, P. J. & Chen, P. H. DNA detection using commercial mobile phones. Biosens. Bioelectron. 26, 4349–4354 (2011).
Lv, S., Zhang, K. & Tang, D. A new visual immunoassay for prostate-specific antigen using near-infrared excited CuxS nanocrystals and imaging on a smartphone. Analyst 144, 3716–3720 (2019).
Wang, L.-J., Chang, Y.-C., Sun, R. & Li, L. A multichannel smartphone optical biosensor for high-throughput point-of-care diagnostics. Biosens. Bioelectron. 87, 686–692 (2017).
Dutta, S., Saikia, K. & Nath, P. Smartphone based LSPR sensing platform for bio-conjugation detection and quantification. RSC Adv. 6, 21871–21880 (2016).
Romeo, A., Leung, T. S. & Sánchez, S. Smart biosensors for multiplexed and fully integrated point-of-care diagnostics. Lab Chip 16, 1957–1961 (2016).
Ghatpande, N. S. et al. Development of a novel smartphone-based application for accurate and sensitive on-field hemoglobin measurement. RSC Adv. 6, 104067–104072 (2016).
Meng, X. et al. Smartphone based hand-held quantitative phase microscope using the transport of intensity equation method. Lab Chip 17, 104–109 (2017).
Xu, G. et al. Passive and wireless near field communication tag sensors for biochemical sensing with smartphone. Sens. Actuators B Chem. 246, 748–755 (2017).
Calabria, D. et al. Smartphone–based enzymatic biosensor for oral fluid L-lactate detection in one minute using confined multilayer paper reflectometry. Biosens. Bioelectron. 94, 124–130 (2017).
Yang, J.-S., Shin, J., Choi, S. & Jung, H.-I. Smartphone Diagnostics Unit (SDU) for the assessment of human stress and inflammation level assisted by biomarker ink, fountain pen, and origami holder for strip biosensor. Sens. Actuators B Chem. 241, 80–84 (2017).
Martinez, A. W. et al. Simple telemedicine for developing regions: camera phones and paper-based microfluidic devices for real-time, off-site diagnosis. Anal. Chem. 80, 3699–3707 (2008).
Zhu, H., Mavandadi, S., Coskun, A. F., Yaglidere, O. & Ozcan, A. Optofluidic fluorescent imaging cytometry on a cell phone. Anal. Chem. 83, 6641–6647 (2011).
Kurzawski, G. et al. DNA and RNA analyses in detection of genetic predisposition to cancer. Hered. Cancer Clin. Pract. 10, 17 (2012).
Luka, G. et al. Label free interdigitated capacitive biosensor for the detection of Cryptosporidium. In 20th International Conference on Miniaturized Systems for Chemistry and Life Sciences, MicroTAS 2016 (2016).
Miller, J. N. Basic statistical methods for analytical chemistry. Part 2. Calibration and regression methods. A review. Analyst 116, 3–14 (1991).
Sorouraddin, M. H., Amini, K., Naseri, A. & Rashidi, M. R. Simultaneous spectrophotometric determination of phenanthridine, phenanthridinone and phenanthridine N-oxide using multivariate calibration methods. Cent. Eur. J. Chem. 8, 207–213 (2010).
Baeumner, A. J., Pretz, J. & Fang, S. A universal nucleic acid sequence biosensor with nanomolar detection limits. Anal. Chem. 76, 888–894 (2004).
Lesnik, E. A. & Freier, S. M. Relative thermodynamic stability of DNA, RNA, and DNA:RNA hybrid duplexes: Relationship with base composition and structure. Biochemistry 34, 10807–10815 (1995).
Chalmers, R. M., Campbell, B. M., Crouch, N., Charlett, A. & Davies, A. P. Comparison of diagnostic sensitivity and specificity of seven Cryptosporidium assays used in the UK. J. Med. Microbiol. 60, 1598–1604 (2011).
Ware, M. W., Keely, S. P. & Villegas, E. N. Development and evaluation of an off-the-slide genotyping technique for identifying Giardia cysts and Cryptosporidium oocysts directly from US EPA Method 1623 slides. J. Appl. Microbiol. 115, 298–309 (2013).
Elsafi, S. H. et al. Comparison of microscopy, rapid immunoassay, and molecular techniques for the detection of Giardia lamblia and Cryptosporidium parvum. Parasitol. Res. 112, 1641–1646 (2013).
Luka, G. On-chip-based biosensors and point-of-care devices for label/PCR-free detection of Cryptosporidium. (2021).
Elgun, G. & Koltas, I. S. Investigation of Cryptosporidium spp. antigen by ELISA method in stool specimens obtained from patients with diarrhea. Parasitol. Res. 108, 395–397 (2011).
Danišová, O., Halánová, M., Valenčáková, A. & Luptáková, L. Sensitivity, specificity and comparison of three commercially available immunological tests in the diagnosis of Cryptosporidium species in animals. Braz. J. Microbiol. 49, 177–183 (2018).
Elwin, K. et al. A comparison of two approaches to extracting Cryptosporidium DNA from human stools as measured by a real-time PCR assay. J. Microbiol. Methods 89, 38–40 (2012).
Le Govic, Y. et al. Assessment of microscopic and molecular tools for the diagnosis and follow-up of cryptosporidiosis in patients at risk. Eur. J. Clin. Microbiol. Infect. Dis. 35, 137–148 (2016).
Adeyemo, F. E., Singh, G., Reddy, P. & Stenström, T. A. Methods for the detection of Cryptosporidium and Giardia: From microscopy to nucleic acid based tools in clinical and environmental regimes. Acta Trop. 184, 15–28 (2018).
Bitilinyu-Bangoh, J. et al. Performance of three rapid diagnostic tests for the detection of Cryptosporidium spp. and Giardia duodenalis in children with severe acute malnutrition and diarrhoea. Infect. Dis. Poverty 8, 96 (2019).
Costa, D. et al. Comparative performance of eight PCR methods to detect cryptosporidium species. Pathogens 10, 1–11 (2021).
Ertürk, G. & Mattiasson, B. Capacitive biosensors and molecularly imprinted electrodes. Sens. (Basel). 17, 390 (2017).
Thiruppathiraja, C., Saroja, V., Kamatchiammal, S., Adaikkappan, P. & Alagar, M. Development of electrochemical based sandwich enzyme linked immunosensor for Cryptosporidium parvum detection in drinking water. J. Environ. Monit. 13, 2782–2787 (2011).
Monzó, J., Insua, I., Fernandez-Trillo, F. & Rodriguez, P. Fundamentals, achievements and challenges in the electrochemical sensing of pathogens. Analyst 140, 7116–7128 (2015).
Dziąbowska, K. Application of Electrochemical Methods in Biosensing Technologies. In (ed. Czaczyk, E.) Ch. 10 (IntechOpen, 2018). https://doi.org/10.5772/intechopen.72175.
Cesewski, E. & Johnson, B. N. Electrochemical biosensors for pathogen detection. Biosens. Bioelectron. 159, 112214 (2020).
Nejadmansouri, M., Majdinasab, M., Nunes, G. S. & Marty, J. L. An overview of optical and electrochemical sensors and biosensors for analysis of antioxidants in food during the last 5 years. Sensors (Switzerland) vol. 21 (2021).
Nguyen, H. H., Park, J., Kang, S. & Kim, M. Surface plasmon resonance: a versatile technique for biosensor applications. Sens. (Basel). 15, 10481–10510 (2015).
Damborsky, P., Vitel, J. & Katrlik, J. Optical biosensors. Essays Biochem. 60, 91–100 (2016).
Chen, C. & Wang, J. Optical biosensors: An exhaustive and comprehensive review. Analyst 145, 1605–1628 (2020).
Prabowo, B. A., Purwidyantri, A. & Liu, K.-C. Surface plasmon resonance optical sensor: A review on light source technology. Biosensors 8, 80 (2018).
Shrivastav, A. M., Cvelbar, U. & Abdulhalim, I. A comprehensive review on plasmonic-based biosensors used in viral diagnostics. Commun. Biol. 4, 70 (2021).
Liu, B., Zhuang, J. & Wei, G. Recent advances in the design of colorimetric sensors for environmental monitoring. Environ. Sci. Nano 7, 2195–2213 (2020).
Pohanka, M. Colorimetric hand-held sensors and biosensors with a small digital camera as signal recorder, a review. Rev. Anal. Chem. 39, 20–30 (2020).
Zhang, F. & Liu, J. Label-free colorimetric biosensors based on aptamers and gold nanoparticles: A critical review. Anal. Sens. 1, 30–43 (2021).
Zhao, V. X. T., Wong, T. I., Zheng, X. T., Tan, Y. N. & Zhou, X. Colorimetric biosensors for point-of-care virus detections. Mater. Sci. Energy Technol. 3, 237–249 (2020).
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G.S.L. originated the idea and designed the experiments, performed the experiments, analyzed the data, selected reagents/materials/analysis tools, wrote the manuscript, prepared figures and tables, and reviewed drafts of the manuscript. E.N. reviewed drafts of the manuscript. Q.T. helped in the three-dimensional modelling and printing of the 3D holder. N.T. reviewed drafts of the manuscript. H.N. and M.H. contributed to the development of the device, commented on the design of the experiment and reviewed the manuscript and oversaw the project.
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Luka, G.S., Nowak, E., Toyata, Q.R. et al. Portable on-chip colorimetric biosensing platform integrated with a smartphone for label/PCR-free detection of Cryptosporidium RNA. Sci Rep 11, 23192 (2021). https://doi.org/10.1038/s41598-021-02580-w
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DOI: https://doi.org/10.1038/s41598-021-02580-w
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