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# Analysis of Parasitic Protozoa at the Single-cell Level using Microfluidic Impedance Cytometry

## Abstract

At present, there are few technologies which enable the detection, identification and viability analysis of protozoan pathogens including Cryptosporidium and/or Giardia at the single (oo)cyst level. We report the use of Microfluidic Impedance Cytometry (MIC) to characterise the AC electrical (impedance) properties of single parasites and demonstrate rapid discrimination based on viability and species. Specifically, MIC was used to identify live and inactive C. parvum oocysts with over 90% certainty, whilst also detecting damaged and/or excysted oocysts. Furthermore, discrimination of Cryptosporidium parvum, Cryptosporidium muris and Giardia lamblia, with over 92% certainty was achieved. Enumeration and identification of (oo)cysts can be achieved in a few minutes, which offers a reduction in identification time and labour demands when compared to existing detection methods.

## Introduction

The protozoan pathogens Cryptosporidium and Giardia are responsible for a large, global disease burden which affects the health of both humans and livestock and, in turn, has a significant knock-on economic impact1,2,3. Globally, the human disease burden for Cryptosporidium is estimated at 250–500 million cases per year1. A waterborne outbreak of cryptyosporidiosis in Milwaukee in 1993 infected 400,000 people with a cost of \$96 million3, 4 and outbreaks have occurred more recently in Australia5, the UK6 and Sweden7. In the UK, an outbreak of Cryptosporidium in Lancashire, beginning August 2015, is estimated to have affected 300,000 households over a six-week period with a cost of approx. £15 m6. With the global population continuing to rise, the intensification of farming and the growing demand for potable drinking-water will ﻿li﻿kely lead to an increase in the incidence of disease in humans and animals1, 4. Food- and water-borne pathogens are therefore of growing concern to governments and industry worldwide.

Cryptosporidium oocysts are produced in high numbers, highly infective, persistent in water, resistant to chlorination, deformable and able to evade modern filtration systems in low numbers2, 4, 8,9,10,11,12. With fewer than 10 oocysts capable of initiating a significant human infection13, 14, waterborne monitoring for the presence of this pathogen is therefore essential15, 16. The standard method of isolation and detection for Cryptosporidium oocysts present in treated water supplies, EPA 1623.117, typically involves the processing of 50–100 L of water (e.g., on site) or 1000 L (e.g., at the treatment works) to a 50 µL volume, before highly-skilled microscopists confirm detection using specialised techniques18. This process also simultaneously recovers cysts of the Giardia genus – protozoan parasites that may also cause gastroenteritis if ingested by humans17.

The ability to rapidly enumerate and discriminate Cryptosporidium oocysts (e.g., post-recovery via EPA 1623.1) based on viability status and/or species in an automated process would reduce detection time, reduce the level of human intervention required, aid in better assessing the risk posed to human health and contribute to the saving of resources19. To discern between live and temperature-inactivated oocysts, the intrinsic electrical properties of single C. parvum have been measured using AC electrokinetic techniques such as dielectrophoresis20, 21 and/or electrorotation22, 23. Measurements were either performed in batch20, 22, 23, required long processing times21 or required microscopy to assess the oocyst response to an applied field20,21,22,23. AC electrokinetic techniques have been utilised for sorting at the genus level, e.g. Cryptosporidium and Giardia. Unni et al.24 demonstrated dielectrophoretic separation of Cryptosporidium muris and Giardia lamblia on-chip in batch mode, but did not report a limit of detection. However, such approaches have not, to our knowledge, been used for the discrimination of alternate species of Cryptosporidium and it has been suggested that the separation of C. parvum and C. muris might not be possible, as both show only minor difference in dielectric properties24.

The only use of an electrical impedance analysis system to characterise the electrical properties of viable and non-viable C. parvum oocysts was demonstrated by Houssin et al.25. Results showed a 15% difference in impedance magnitude with a low conductivity buffer containing either viable or non-viable C. parvum, with a reported detection limit <10 oocysts µL−1. Measurements were made in bulk, where aliquots containing oocysts, either viable or non-viable, were loaded into sample wells, with the impedance measured and compared to the control (previously measured values of the suspending fluid alone). However, oocysts in any real sample, e.g., those recovered using EPA 1623.1, could be of mixed viability; therefore, it is a necessity that any impedance system used for detection can discern the viability status of single oocysts. To our knowledge, there are no reports of the impedance analysis of different Cryptosporidium species, or the simultaneous impedance analysis of Cryptosporidium and Giardia.

Microfluidic Impedance Cytometry (MIC) is a microfluidic system that uses microelectrodes to measure the impedance of single particles26, 27. Suspended particles flow through a microchannel at high speed (flow rates up to ~80 µL min−1 can be used) and as they pass a detection region, the measured current gives a signal which is proportional to particle impedance. This method is label-free, requires minimal sample processing and measures up to 1000 particles per second28. In comparison to other continuous microfluidic separation/discrimination technologies29, 30, MIC offers rapid sample processing and high throughput. MIC has been used for discriminating various cell types including stem cells31, leukocytes32, 33 and tumour cells in whole blood34. However, the applicability of MIC to the detection of parasitic protozoa has not yet been widely explored and previous work has focussed on analysis of infected cells rather than direct protozoan analysis35, 36.

In this paper, we describe the use of MIC to detect single protozoan (oo)cysts within a continuous flow system. We characterise the biophysical properties of live and temperature-inactivated, human-pathogenic parasites and assess sample composition by analysing the electrical data. We also detect single C. parvum and C. muris oocysts, as well as G. lamblia cysts. Detection and viability/species analysis of oocysts in continuous flow using MIC offers a significant advance over other approaches, both in terms of gathering information at the single (oo)cyst level and the speed of data collection.

## Materials and Methods

### System Overview

The microfluidic impedance chips were fabricated as described previously29, 34, 37 using photolithography and full wafer thermal bonding. In short, platinum electrodes (30 µm width and 200 nm thickness) were patterned on a glass wafer. Microchannels, with cross-sectional dimensions 200 µm × 30 µm leading into a detection region of 40 µm × 30 µm, were defined in SU8 photoresist before thermal bonding of two wafers. After dicing, inlet and outlet channels were etched using a CO2 laser (Mini 18, Epilog Laser). The chips were held in a 3D-printed holder, which housed fluidic attachments and electrical connections. The holder was mounted on an x-y-z stage with optics to image the detection region. A syringe pump (Fusion 400, Chemyx) was used to introduce the sample from a syringe at a flow rate of 40 µL min−1.

Figure 1 shows a diagram of the impedance chip. Sinusoidal voltages at two simultaneous frequencies were applied to the top two electrodes using a digital impedance analyser (H2FLI, Zurich Instruments). The first frequency, termed the reference frequency, was applied at 18.3 MHz, while the second (probe) frequency was varied in the range 250 kHz to 50 MHz (Fig. 1). The voltage ranged from 1.5 Vpp to 10 Vpp depending on buffer conductivity and signal frequency. At frequencies above 20 MHz the signals are attenuated by the input and output filters of the lock-in amplifier, reaching −6dB at 50 MHz. Therefore, for frequencies ≥20 MHz, the applied voltage was increased incrementally to account for this attenuation. The average signal magnitude for the nearest 3 probe frequencies below 20 MHz was first calculated$$\,({\bar{Z}}_{ < 20MHZ})$$. Then, the gain was calculated by dividing this average value by the average magnitude signal for each frequency (e.g. $$facto{r}_{50MHZ}=\,{\bar{Z}}_{ < 20MHZ}/{\bar{Z}}_{50MHZ}$$ for 50 MHz). An example can be found in Supplementary Fig. S1. Increasing the voltage minimized signal loss without affecting data collection or analysis. At any one probe frequency, data was recorded for approximately 30 s, before the probe frequency was increased. The current flowing through both bottom electrodes was converted to voltage using transimpedance amplifiers. A differential amplifier was used to retrieve a single output signal. Lock-in amplification (HF2LI, Zurich Instruments) was used to separate the magnitude and phase at each frequency, from which impedance scatter plots were generated.

Between samples, the chips were flushed with 1 mL ethanol (70%) and 1 mL DI water using a syringe. Electrode surfaces were cleared of debris on a daily basis by introducing 1 M sodium hydroxide into the system at 50 µL min−1 for ~4 mins, before rinsing with 1 mL DI water.

### Sample Preparation

Four different stock samples were used in our analysis of untreated and heat-inactivated C. parvum. These samples, all obtained in suspensions containing PBS + 2% antibiotics + 0.01% Tween 20, were as follows:

• A batch of calf-sourced C. parvum (WC1) obtained from Waterborne Inc. (Iowa strain; US) was used within one month of propagation.

• A second batch of calf-sourced C. parvum (WC2) and a batch of mouse-sourced C. parvum (WM) from Waterborne Inc. (Iowa strain) were used within 1–2 months of oocyst propagation.

• Calf-sourced C. parvum (MC) obtained for Moredun Scientific (Moredun Strain; UK) were used when aged approximately 2–3 months.

From each stock, samples containing untreated or heat-inactivated C. parvum were independently prepared and the impedance measured separately. In each sample, oocysts were diluted to a final concentration of ~100 oocysts µL−1 of PBS. The effect of varying buffer conductivity was examined using different PBS concentrations, ranging from 0.76–7.10 S m−1. Each buffer also contained 0.1% Tween 20. Calibration polystyrene beads of 7 µm diameter (Microparticles GmbH) were added to each sample to a final concentration of 100 beads µL−1. Polystyrene beads have a known size and electrical properties34, and have a constant impedance across the frequency range used in these experiments. The measured impedance signal of each oo(cyst) was normalised with respect to the bead by dividing by the mean impedance of the polystyrene beads for each frequency, thus removing any non-linearities.

For impedance analysis of live Cryptosporidium spp. and G. lamblia, individual samples containing either C. parvum, C. muris or G. lamblia (obtained from Waterborne Inc.) were prepared in PBS + 0.1% Tween 20 (σm = 1.6 S m−1). Mixed samples were diluted to contain a total of ~100 (oo) cysts and 100 beads µL−1 of sample; mixed samples were prepared to include equal numbers of each pathogen. All samples were introduced to the system and measured as described previously.

### Oocyst Inactivation

In order to inactivate oocysts, samples prepared as described for untreated C. parvum in the previous section were subjected to heat-treatment at 70 °C for 5 mins in a heating block (Stuart Scientific, UK) before measurement. This treatment is reported in the literature as the minimum treatment required to induce loss of infectivity in the mouse model20, 38.

### Data Analysis

A custom script was written in Matlab (R2016a) for data processing and statistical analysis. In order to make reliable statistical inference regarding each population, samples containing each population were first measured separately. Using the comparison of untreated and heat-inactivated C. parvum as an example, the impedance signal was first normalised relative to the frequency-independent impedance response of the polystyrene beads. Then the C. parvum oocyst populations were gated from smaller debris and the larger reference beads using normalised impedance data gathered at the reference frequency (18.3 MHz). Upon gating, the normalised impedance response of gated pathogens at probe frequency were then be plotted and analysed.

By considering the spread and orientation of the data and assuming normal data distribution, it was possible to estimate the level of discrimination achieved across both impedance dimensions (real and imaginary, or opacity and size), at a given frequency, between any two populations. Firstly, the covariance matrix was calculated to identify the directions in which the 2-D data of a single population varied most – the largest and smallest eigenvectors of this matrix indicate the direction of the data spread and the magnitude of this spread was given by the eigenvalues of the matrix. Secondly, with respect to spread and orientation of each population, confidence ellipses containing all events within 1–3 standard deviations of the mean were plotted to identify the positions of equal probability deviation between two clusters, i.e the intersection of the equivalent confidence ellipses defines the boundary where a data point has equal probability of belonging to either population. A line of equal probability deviation was then fitted to the points of intersection and subsequently, the discrimination confidence was indicated – i.e., by counting the number of oocysts from each population that plotted either side of the line of equal probability deviation.

### Excystation Assay

The viability rates of the live C. parvum stock samples were estimated using an in vitro excystation assay developed at Moredun Research Institute (UK)39, to evaluate original stock sample quality and provide a reference for comparison of untreated and heat-inactivated C. parvum. Upon completion of the assay, oocysts were visualised using a differential interference contrast (DIC) microscope (BX50, Olympus) and the number of intact oocysts and empty shells were counted until 250 events had been recorded. For each sample, three counts were performed. The following formula was used to calculate excystation percentage: number of empty shells/(number of empty shells + number intact oocysts). The average sample viability rates for the original C. parvum stock samples were: 95% for WC1, 86% for WC2; 87% for WM; and 88% for MC. Please see Table S1 for more detailed excystation assay results.

### Optical Flow Cytometry

Conventional flow cytometric analysis of parasite suspensions was carried out at 35 µL min−1 using a BD Accuri C6 flow cytometer (BD Biosciences) with two lasers (488 nm and 640 nm). Data were exported as standard FCS files and the forward and side scattered light (FSC and SSC) signals were analysed using Matlab.

### Data availability

All data supporting this study are openly available from the University of Southampton repository at http://doi.org/10.5258/SOTON/D0047.

## Results and Discussion

### Dielectric properties

The simplest electrical model that describes the properties of a cell is the so called single-shelled model as shown in Fig. 2(a). Generally, biological cells are insulating at low frequencies (kHz), due to the presence of the lipid cell membrane, but become increasingly conductive at higher frequencies (MHz) due to capacitive coupling across the membrane25, 34, 40. Therefore, for a viable cell, the impedance at low frequencies (<1 MHz) measures cell volume, while intermediate frequencies (0.5–10 MHz) measures membrane capacitance, which reflects membrane invagination and convolution. At higher frequencies, the electric field capacitively couples across the membrane and the impedance signal reflects the cytoplasm properties and any nucleus which may be present. Figure 2(b) illustrates the specific case for an oocyst which contains four nuclei-containing sporozoites and various organelles. By analogy with a typical cell, at low frequencies only the volume of the intact oocysts can be measured. In the MHz regime, oocyst impedance firstly becomes a function of the outer wall capacitance (typically at frequencies 1–10 MHz) before the conductivity of the interior strongly influences the response at high frequencies (>10 MHz)27. Consequently, in the intermediate frequency range viable oocysts of equivalent size may show differences in their impedance due to variations in the composition and/or structure of the outer wall and the interior. As the signal frequency increases further, i.e., >30 MHz, the impedance is further influenced by the sporozoites and nuclei27.

The disruption of the selectively permeable membrane of a biological cell is typically measured using a viability stain such as Propidium Iodide (PI). Upon entering cells with compromised membranes, PI binds to DNA, intercalating between the bases which increases the fluorescence significantly. If a compromised cell membrane is permeable to PI, ions will be able to move freely across (i.e., the cell is electrically leaky, Fig. 3), which manifests as changes in the low frequency impedance34. Therefore, non-viable cells may appear smaller in electrical volume but not optical volume. Non-viable cells become incapable of regulating ion transfer and maintaining osmotic pressure as efficiently as viable cells34, 41, as, in the case of a C. parvum oocyst, is shown diagrammatically in Fig. 3a. A contributing factor in the ability of viable oocysts to persist in the environment for long durations is their strict regulation of ion transfer. Upon inactivation, oocysts no longer regulate ion transfer as efficiently as viable oocysts. Thus, the internal composition of the inactivated oocyst may become compromised. For example, the microscope images of untreated (Fig. 3b) and heat-inactivated (Fig. 3c) C. parvum show that the interior constituents appear less granular in heat-inactivated oocysts, which may indicate a change in their internal composition. Therefore, by suspending oocysts in non-isosmotic conditions, it may be possible to induce change in the ionic composition of an oocyst and consequently change its intermediate and/or high frequency impedance.

### Impedance Analysis of Parasites

Figure 4 shows experimental impedance data for four different untreated C. parvum populations suspended in 0.5 × PBS (σm = 0.76 S m−1), at a reference frequency of 18.3 MHz. A high reference frequency was selected so that the internal properties of the oocysts could be probed31, 34. Impedance magnitude (|Z|) is plotted on the x-axis and impedance phase (ΦZ) on the y-axis, where each data point represents a single oocyst and its colour reflects the data density.

With environmental aging, e.g., exposure to natural stress like UV light and temperature variations or alternatively, sample transit and processing when used in a laboratory setting, some oocysts may become collapsed, distorted or even excysted42. In these cases, the infective sporozoites may be lost and consequently oocysts become “empty shells” or “ghosts”. Empty shells are routinely detected in environmental drinking-water samples43 and the impedance data in Fig. 4 shows the presence of such damaged/excysted oocysts. As is demonstrated in the next section, the shells appear as a separate cluster below the main oocyst population and have lower impedance magnitude (as they are electrically leaky) and phase on average. The subplots of Fig. 4a–d are in ascending order of age. Interestingly, the youngest (a) and oldest (d) C. parvum samples have the least and most shells present respectively (% shells in a = 6, b = 6, c = 8 and d = 41), which implies that the number of shells increases with environmental age.

### Impedance Modelling

Generally, the dielectric behaviour of biological cells in suspension is defined by Maxwell’s mixture theory (MMT)44, which describes the relation between the complex impedance of the suspension, the cell properties, the suspending medium and the volume fraction45. Based on MMT, shell-based models have been used to model the dielectric properties of cells45,46,47. Single shell models describe cells with just a membrane and no interior (see Fig. 2), and double shell models are applied for more complex cells with interior organelles. The frequency-dependent behaviour of these models can be plotted in terms of Debye relaxations48. Single shells have a single relaxation and double shells have two (the first associated with the cell membrane and the second with the interior organelles, Fig. 2b)27, 45. Thus, the integrity and complexity of a cell can be inferred by fitting data to these models.

The frequency dependent impedance for the average population of untreated and heat-inactivated C. parvum oocysts was measured from 250 kHz to 50 MHz, with a buffer conductivity of σm = 0.76 S m−1 - see Fig. 5. Each data point represents the mean of 1,000 oocysts per probe frequency.

The impedance data for the empty shells in untreated and heat-inactivated C. parvum suspensions was modelled by fitting the data to a single Debye relaxation representing a single shell fit (SSF) – Fig. 5a,b. As expected, the simple structure of the oocyst shell, where no sporozoites or other organelles are present, fits well to a single relaxation. Moreover, heat-inactivation of the suspension results in physical disruption of the membrane, leading to an apparent reduction in the magnitude of the low frequency impedance (Fig. 5a). The main oocyst population could not be fitted to a single shell model (see Supplementary Fig. S2) meaning that this model does not fully represent the intricacies of the oocyst structure. The double shell model however, provides a good fit as shown in Fig. 5c,d, i.e., it correctly represents the relaxation the oocyst membrane (~1–10 MHz) followed by the relaxation of the interior content (>10 MHz). Furthermore, as seen for the shells, heat-inactivation and consequent outer wall disruption causes a small drop in low frequency impedance (Fig. 5c). Thus, the simple model confirms that the two populations (Fig. 4) are correctly identified and that the C. parvum shells can be excluded from future analysis of the oocysts.

### Optimal Suspension Conductivity

The average impedance of all untreated and heat-inactivated C. parvum populations suspended in a buffer of conductivity (σm = 1.51 S m−1) is shown in Fig. 6a,b. With increasing buffer conductivity, the relaxation frequency of the outer wall shifted towards higher frequencies as expected. Figure 6 also shows that the dielectric properties of untreated and heat-inactivated C. parvum are different, especially at higher frequencies (see Fig. 6c,e), where the signal is influenced by the properties of the oocyst interior. Generally, the C. parvum oocyst interior consists of four (nuclei-containing) sporozoites – the infective agents of the oocyst – and a membrane-enclosed residual body. The residual body contains a large lipid body, numerous amylopectin granules, a crystalline protein inclusion, ribosomes and cytomembranes4. For heat-inactivated C. parvum, the integrity and/or composition of the internal fluid and interior organelles was presumably compromised, and the osmolality difference between the oocyst interior and suspending medium was greater in 1xPBS than the 0.5x PBS buffer (σm = 0.76 S m−1) – see Fig. 5c,d. Thus, the difference in the high frequency impedance of the parasite populations was greater for those re-suspended in PBS (Fig. 6). These findings suggest that the parasites were exposed to hyperosmotic conditions when suspended in PBS. The data in Fig. 6a,b also indicates no difference in either the magnitude or phase, regardless of strain or source of the C. parvum oocysts.

The suspension of oocyst populations in a high conductivity, hyperosmotic buffer (5x PBS; σm = 7.10 S m−1) gave rise to the largest difference in the impedance of untreated and heat-inactivated C. parvum. Figure 7 shows the low, intermediate and high frequency impedance of C. parvum in 5x PBS. High frequency impedance enables the clearest discrimination of the parasite populations and this difference is enhanced by increasing suspending medium conductivity. The green line indicates the line of equal probability deviation between the populations (i.e., where a detected event has equal chance of belonging to either population) and is an estimate of confidence in the discrimination between untreated and heat-inactivated C. parvum. For example, at 50 MHz, where the clearest discrimination was achieved (Fig. 7c), 91% of the events to the right of the equal probability boundary were from the untreated C. parvum population and 92% of the events to the left were from the heat-inactivated C. parvum population. Thus, MIC enabled the identification of untreated or heat-inactivated C. parvum with over 90% confidence in these experimental conditions. The data contained in Table S2 shows the identification confidence achieved for each individual sample and demonstrates that sample age and/or sample viability negatively affects the discrimination level.

### Species Analysis

The impedance of pathogens which are commonly isolated using EPA 1623.1 was measured to assess the suitability of MIC for species- and genus-level discrimination of waterborne parasites. Specifically, samples containing C. parvum (CP), C. muris (CM) and G. lamblia (GL) suspended in PBS (σm = 1.61 S m−1) were analysed. To properly gate and characterise the impedance of each population, samples were firstly measured independently – Supplementary Fig. S3. The cube root of the low frequency impedance magnitude is proportional to particle diameter28, 34. Using this data, the average diameter of the parasites was determined as CP = 4.3 ± 0.3 µm, CM = 5.9 ± 0.4 µm and GL = 9.3 ± 0.4 µm, which correlates well with dimensions obtained from optical imaging49, 50.

The difference in impedance between populations can be visualised in a number of ways, but the clearest discrimination is obtained from a scatter plot of the high frequency phase (at 18.3 MHz) against low frequency impedance magnitude (at 250 kHz), as shown in Fig. 8. This data effectively plots variations in internal structure/composition vs size. The figure shows data for 1,000 events which were obtained by measuring a sample that contained all the different populations. Using the same gates as in Figs 5 and 6, it was possible to identify CP with 98% confidence, CM with 93% confidence and GL with over 99% confidence. These results suggest that impedance analysis allows discrimination of these pathogens with a high degree of confidence, especially when compared to conventional flow cytometry (Fig. 8b).

The two species C. parvum and C. hominis are estimated to be responsible for over 90% of human cases of cryptosporidiosis51. However, other species (C. meleagridis, C. canis, C. cuniculus and C. felis) have also been associated with human infection and are considered “major human-pathogenic species”49, 52. In terms of oocyst dimensions, all these “major” species show similarity and are typically reported as elliptical oocysts within the size range of 4.0–5.0 × 5.0–5.5 µm49. Our results suggest that MIC may be able to discriminate oocysts of this size, with a high degree of certainty, from other species of Cryptosporidium that are not within this size range and which pose little or no risk to human health (as we have demonstrated with C. parvum and C. muris). Such species include (but not limited to) the larger C. andersoni, C. baileyi and C. muris, plus the smaller C. xiaoi and C. ryanae 49, which were all identified among the low-risk, contaminating species of UK drinking-water over a one-year period53. However, analysis of distinct species which have similar dimensions is required to assess whether inter-species variations in oocyst wall and interior structure/composition may facilitate impedance-based discrimination of such oocysts.

## Conclusion and Outlook

Utilisation of MIC offers for the first time the ability to assess the species and viability status at the single (oo)cyst level, with the additional advantages of rapid automated processing and a label-free, non-destructive method. The impedance properties of C. parvum oocysts of varying source, strain and age were measured in buffers of different conductivity. The impedance data of the oocyst and shell populations within each sample were fitted to either a single or double shell model. The results indicated that it was possible to identify the presence of damaged/excysted oocysts (termed shells) and that shell numbers increased with environmental age.

The ability of MIC to probe different layers of the oocyst structure means that impedance analysis enables clearer discrimination than optical flow cytometry – an equivalent, label-free method (see Supplementary Fig. S4). The data shows that untreated and heat-inactivated C. parvum can be identified with over 90% certainty at high frequencies when suspended in 5x PBS. It is hypothesised that the contrast is best in this conductivity because the non-viable parasite loses the ability to regulate ion transfer, resulting in an inward flux of ions which increases the electrical “contrast” between untreated and heat-inactivated C. parvum. In addition, single C. parvum, C. muris and G. lamblia (oo) cysts were identified with over 92% certainty from the high frequency phase vs low frequency magnitude data (when suspended in PBS).

This technology could potentially be useful for water utilities in, e.g., a warning system which more rapidly identifies single Cryptosporidium and Giardia (oo)cysts post-recovery via EPA 1623.1. As demonstrated, the system can also simultaneously provide an indication of the viability and species of recovered (oo)cysts, which may reduce the requirement for skilled microscopists and the associated labour demands. This system could also be used for foodborne protozoan monitoring or the analysis of veterinary or clinical samples.

For widespread use of this technique in, e.g., water monitoring, this study should be extended to demonstrate that Cryptosporidium oocysts which have been inactivated by means other than heat-inactivation can also be discriminated from viable oocysts. Future work should also assess the suitability of MIC for discriminating other species of Cryptosporidium, which pose/do not pose a significant risk to human health as well as characterise the performance with (oo)cysts from different matrices, including water, food and faecal samples. The method should also be compared for replacement of the “gold standard” animal infectivity protocols.

Subject to further validation with environmental samples, this technology could be implemented into the existing regulatory framework for waterborne protozoan monitoring to enable rapid assessment of oocyst viability and thus provide a more accurate assessment of the risk posed to human health. For example, the existing detection method utilises immuno-magnetic separation (IMS) for parasite enrichment, giving a ~50 µL volume with recovered oocysts16. By increasing the conductivity of this product sample, it may be possible to discern between untreated and heat-inactivated C. parvum using MIC. The system could operate at an increased flow rate28, therefore it would be possible to process a sample in much less than an hour. Finally, it is also possible to view results in real-time, which would allow water utilities to rapidly identify potentially hazardous drinking-water.

All data supporting this study are openly available from the University of Southampton repository at http://doi.org/10.5258/SOTON/D0047.

Publisher's note: Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

## References

1. 1.

World Health Organization. Guidelines for Drinking-water Quality - Fourth Edition. (World Health Organization, 2011).

2. 2.

Davies, A. P. & Chalmers, R. M. Cryptosporidiosis. British Medical Journal 339, doi:10.1136/bmj.b4168 (2009).

3. 3.

Jex, A. R., Smith, H. V., Monis, P. T., Campbell, B. E. & Gasser, R. B. Cryptosporidium — Biotechnological advances in the detection, diagnosis and analysis of genetic variation. Biotechnology Advances 26, 304–317 (2008).

4. 4.

Fayer, R. & Xiao, L. Cryptosporidium and Cryptosporidiosis, Second Edition. (Taylor & Francis, 2012).

5. 5.

Dale, K., Kirk, M., Sinclair, M., Hall, R. & Leder, K. Reported waterborne outbreaks of gastrointestinal disease in Australia are predominantly associated with recreational exposure. Australian and New Zealand journal of public health 34, 527–530 (2010).

6. 6.

Elliot, A. J. et al. The potential impact of media reporting in syndromic surveillance: an example using a possible Cryptosporidium exposure in North West England, August to September 2015. Eurosurveillance 21 (2016).

7. 7.

Widerström, M. et al. Large outbreak of Cryptosporidium hominis infection transmitted through the public water supply, Sweden. Emerging infectious diseases 20, 581–589 (2014).

8. 8.

Šlapeta, J. Cryptosporidiosis and Cryptosporidium species in animals and humans: A thirty colour rainbow? International Journal for Parasitology 43, 957–970 (2013).

9. 9.

Smith, H. V. & Nichols, R. A. B. Cryptosporidium: Detection in water and food. Experimental Parasitology 124, 61–79 (2010).

10. 10.

Chen, F., Huang, K., Qin, S., Zhao, Y. & Pan, C. Comparison of viability and infectivity of Cryptosporidium parvum oocysts stored in potassium dichromate solution and chlorinated tap water. Veterinary parasitology 150, 13–17 (2007).

11. 11.

Byrd, T. & Walz, J. Interaction force profiles between Cryptosporidium parvum oocysts and silica surfaces. Environmental science & technology 39, 9574–9582 (2005).

12. 12.

McGrath, J. S. et al. Deformability Assessment of Waterborne Protozoa Using a Microfluidic-Enabled Force Microscopy Probe. PLoS One 11, e0150438 (2016).

13. 13.

Okhuysen, P. C., Chappell, C. L., Crabb, J. H., Sterling, C. R. & DuPont, H. L. Virulence of three distinct Cryptosporidium parvum isolates for healthy adults. The Journal Of Infectious Diseases 180, 1275–1281 (1999).

14. 14.

King, B. J. & Monis, P. T. Critical processes affecting Cryptosporidium oocyst survival in the environment. Parasitology 134, 309–323 (2007).

15. 15.

Scottish Water. Annual Water Quality Report 2013. (Scottish Water, 2013).

16. 16.

Environment and Heritage Service. Guidance for the Monitoring of Cryptosporidium in Treated Water Supplies in Northern Ireland. (Environment and Heritage Service, 2003).

17. 17.

USEPA. Method 1623.1: Cryptosporidium and Giardia in Water by Filtration/IMS/FA. (United States Environmental Protection Agency, 2012).

18. 18.

Bridle, H. et al. Detection of Cryptosporidium in miniaturised fluidic devices. Water research 46, 1641–1661 (2012).

19. 19.

Bridge, J. W. et al. Engaging with the water sector for public health benefits: waterborne pathogens and diseases in developed countries. Bulletin of the world Health Organization 88, 873–875 (2010).

20. 20.

Su, Y.-H. et al. Quantitative dielectrophoretic tracking for characterization and separation of persistent subpopulations of Cryptosporidium parvum. Analyst 139, 66–73 (2014).

21. 21.

Quinn, C., Archer, G., Betts, W. & O’Neill, J. Dose-dependent dielectrophoretic response of Cryptosporidium oocysts treated with ozone. Letters in applied microbiology 22, 224–228 (1996).

22. 22.

Goater, A. D., Burt, J. P. & Pethig, R. A combined travelling wave dielectrophoresis and electrorotation device: applied to the concentration and viability determination of Cryptosporidium. Journal of Physics D-Applied Physics 30, L65 (1997).

23. 23.

Dalton, C., Goater, A., Burt, J. & Smith, H. Analysis of parasites by electrorotation. Journal of Applied Microbiology 96, 24–32 (2004).

24. 24.

Unni, H. N. et al. Characterization and separation of Cryptosporidium and Giardia cells using on-chip dielectrophoresis. Biomicrofluidics 6, 012805 (2012).

25. 25.

Houssin, T., Follet, J., Follet, A., Dei-Cas, E. & Senez, V. Label-free analysis of water-polluting parasite by electrochemical impedance spectroscopy. Biosensors and bioelectronics 25, 1122–1129 (2010).

26. 26.

Morgan, H., Sun, T., Holmes, D., Gawad, S. & Green, N. G. Single cell dielectric spectroscopy. Journal of Physics D: Applied Physics 40, 61 (2007).

27. 27.

Sun, T. & Morgan, H. Single-cell microfluidic impedance cytometry: a review. Microfluidics and Nanofluidics 8, 423–443 (2010).

28. 28.

Spencer, D., Elliott, G. & Morgan, H. A sheath-less combined optical and impedance micro-cytometer. Lab on a Chip 14, 3064–3073 (2014).

29. 29.

McGrath, J. S., Jimenez, M. & Bridle, H. Deterministic lateral displacement for particle separation: a review. Lab on a Chip 14, 4139–4158 (2014).

30. 30.

Bhagat, A. A. S. et al. Microfluidics for cell separation. Medical & biological engineering & computing 48, 999–1014 (2010).

31. 31.

Song, H. et al. A microfluidic impedance flow cytometer for identification of differentiation state of stem cells. Lab on a Chip 13, 2300–2310 (2013).

32. 32.

Holmes, D. et al. Leukocyte analysis and differentiation using high speed microfluidic single cell impedance cytometry. Lab on a Chip 9, 2881–2889 (2009).

33. 33.

Han, X., van Berkel, C., Gwyer, J., Capretto, L. & Morgan, H. Microfluidic lysis of human blood for leukocyte analysis using single cell impedance cytometry. Analytical chemistry 84, 1070–1075 (2011).

34. 34.

Spencer, D., Hollis, V. & Morgan, H. Microfluidic impedance cytometry of tumour cells in blood. Biomicrofluidics 8, 064124 (2014).

35. 35.

Küttel, C. et al. Label-free detection of Babesia bovis infected red blood cells using impedance spectroscopy on a microfabricated flow cytometer. Acta tropica 102, 63–68 (2007).

36. 36.

Du, E. et al. Electric impedance microflow cytometry for characterization of cell disease states. Lab on a Chip 13, 3903–3909 (2013).

37. 37.

Holmes, D., She, J. K., Roach, P. L. & Morgan, H. Bead-based immunoassays using a micro-chip flow cytometer. Lab on a Chip 7, 1048–1056 (2007).

38. 38.

Fayer, R. Effect of high temperature on infectivity of Cryptosporidium parvum oocysts in water. Applied and environmental microbiology 60, 2732–2735 (1994).

39. 39.

Blewett, D. In Proceedings of the First International Workshop on Cryptosporidiosis. Edinburgh: The Animal Disease Research Association. 85–95.

40. 40.

Schwan, H. In Engineering in Medicine and Biology Society, 1994. Engineering Advances: New Opportunities for Biomedical Engineers. Proceedings of the 16th Annual International Conference of the IEEE. A70–A71 vol. 71 (IEEE).

41. 41.

Shafiee, H., Sano, M. B., Henslee, E. A., Caldwell, J. L. & Davalos, R. V. Selective isolation of live/dead cells using contactless dielectrophoresis (cDEP). Lab on a Chip 10, 438–445 (2010).

42. 42.

Environment Agency. Methods for the Examination of Waters and Associated Materials. (Environment Agency, 2010).

43. 43.

Kostrzynska, M. et al. Three sample preparation protocols for polymerase chain reaction based detection of Cryptosporidium parvum in environmental samples. Journal of microbiological methods 35, 65–71 (1999).

44. 44.

Maxwell, J. C. A treatise on electricity and magnetism. Vol. 1 (Clarendon press, 1881).

45. 45.

Morgan, H. & Green, N. G. AC Electrokinetics: Colloids and Nanoparticles. (Research Studies Press, 2003).

46. 46.

Miller, R. D. & Jones, T. B. Electro-orientation of ellipsoidal erythrocytes. Theory and experiment. Biophysical journal 64, 1588 (1993).

47. 47.

Sun, T., Green, N. G., Gawad, S. & Morgan, H. Analytical electric field and sensitivity analysis for two microfluidic impedance cytometer designs. Iet Nanobiotechnology 1, 69–79 (2007).

48. 48.

Debye, P. & Falkenhagen, H. Dispersion of the Conductivity and Dielectric Constants of Strong Electrolytes, Phys. Vol. 29 (Z, 1928).

49. 49.

Chalmers, R. M. & Katzer, F. Looking for Cryptosporidium: the application of advances in detection and diagnosis. Trends in Parasitology 29, 237–251 (2013).

50. 50.

LeChevallier, M. W., Norton, W. D. & Lee, R. G. Occurrence of Giardia and Cryptosporidium spp. in surface water supplies. Applied and Environmental Microbiology 57, 2610–2616 (1991).

51. 51.

Bouzid, M., Hunter, P. R., Chalmers, R. M. & Tyler, K. M. Cryptosporidium Pathogenicity and Virulence. Clinical Microbiology Reviews 26, 115–134 (2013).

52. 52.

Fratamico, P., Liu, Y. & Kathariou, S. Genomes of Foodborne and Waterborne Pathogens. (American Society of Microbiology, 2011).

53. 53.

Nichols, R., Connelly, L., Sullivan, C. & Smith, H. Identification of Cryptosporidium species and genotypes in Scottish raw and drinking waters during a one-year monitoring period. Applied and environmental microbiology 76, 5977–5986 (2010).

## Acknowledgements

The authors acknowledge the Science & Technology Facilities Council, EPSRC and the European Commission through the Label-free particle sorting (LAPASO) ITN project from the People Programme (Marie Curie Actions) of the European Union’s Seventh Framework Programme FP7/2007-2013 under REA grant agreement no 607350 ITN for funding. We would also like to thank Scottish Water for their continued support.

## Author information

### Author notes

1. J. S. McGrath and C. Honrado contributed equally to this work.

### Affiliations

1. #### Institute of Biological Chemistry, Biophysics and Bioengineering, School of Engineering and Physical Sciences, Heriot-Watt University, Edinburgh, EH14 4AS, United Kingdom

• J. S. McGrath
•  & H. L. Bridle
2. #### Faculty of Physical Sciences and Engineering and Institute for Life Sciences, University of Southampton, Southampton, SO17 1BJ, United Kingdom

• , D. Spencer
•  & H. Morgan

• B. Horton

### Contributions

D.C. and H.M. designed and manufactured the detection system. J.M., C.H., D.C., H.B. and H.M. conceived and designed the experiments. J.M., C.H. and B.H. performed the experimental work. H.B. and H.M. contributed reagents/materials/analysis tools. J.M., C.H. and D.C. generated the manuscript and produced the figures. D.C. and H.M. analysed the data. J.M., D.C., H.B. and H.M. revised the manuscript.

### Competing Interests

The authors declare that they have no competing interests.

### Corresponding author

Correspondence to H. Morgan.

## Electronic supplementary material

### DOI

https://doi.org/10.1038/s41598-017-02715-y

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