Elsevier

Talanta

Volume 177, 15 January 2018, Pages 176-190
Talanta

Developments of microfluidic paper-based analytical devices (μPADs) for water analysis: A review

https://doi.org/10.1016/j.talanta.2017.08.072Get rights and content

Highlights

  • Microfluidic paper-based analytical devices (μPADs) for water analysis are reviewed.

  • The detection methods used by these devices and their pros and cons are described.

  • Precision and accuracy of µPAD-based water analysis is assessed critically.

  • Ability of µPADs to meet legislative guidelines is discussed.

  • Suitability of µPADs for in-field measurements is examined.

Abstract

Water pollution is a serious environmental problem affecting millions of people, and the demand for frequent water quality monitoring is increasing. The need for analytical platforms that combine high sensitivity, selectivity and accuracy with low cost, portability and user friendliness remains a challenge. Microfluidic paper-based analytical devices (μPADs) are recognised as a powerful analytical platform that can satisfy these requirements.

The aim of this review is to provide a detailed overview of the μPADs that have been developed for the determination of important water quality parameters, such as nutrients, metals and organic contaminants, in a range of waters. A description of the fabrication and detection methods selected for these applications is provided, and the performance of the μPADs with respect to their precision and accuracy is critically assessed. The potential of these devices for real-life applications is also critically examined, particularly if they can determine the concentrations specified in water quality guidelines or the maximum recommended concentrations for various waters, as well as if they are suitable for field applications.

Introduction

The fate of the aquatic environment has become a critical issue globally. Population growth, and urbanisation and industrialisation in most countries have had a deleterious effect on water quality. With more than 50% of the world's population living in cities, and almost 70% expected to be urban by 2050, the pressure on water resources is enormous [1]. While in developing countries, water scarcity is a serious threat to human health, in developed countries water is often taken for granted, and consumed and managed in a haphazard manner. Moreover, anthropogenic activities and poor management of agricultural and industrial wastes (e.g. illicit discharges, runoff) all contribute to the decline in water quality [2].

Hence, in parallel with socioeconomic and political measures, frequent water quality assessment and diligent water management are crucial in order to guarantee safe water supplies to humans, and to identify, control and prevent aquatic pollution. There is thus an urgent need for analytical platforms that can combine high-sensitivity, accuracy and rapid analysis with simplicity, portability and low cost, in order to make water analysis (e.g. of drinking water, freshwater, wastewater) accessible to water scientists and managers, as well as for interested citizen groups.

Microfluidic paper-based analytical devices (µPADs) are recognised as a potentially powerful analytical platform because they embody many of the features listed above. The use of paper as a substrate for analytical purposes has several advantages [3], namely it is readily available and inexpensive, can be easily patterned into discrete hydrophilic and hydrophobic zones using existing printing or cutting technologies, is able to wick fluids by capillary action without external power sources, is lightweight and easy to transport, and is disposable and biodegradable. The antecedents of the paper-based analytical devices date back to the mid-seventeenth century, when Boyle introduced litmus paper as an acid-base indicator [4]. However, since 2007 this methodology has grown exponentially [5] because of Whitesides and co-workers who described a simple method for patterning paper with hydrophobic barriers in order to create well-defined hydrophilic channels [6]. Even though most of the research on µPADs has been focused on point-of-care diagnostic devices [7], other applications have emerged [8], [9], namely in environmental analysis [10] as well as in food and water analysis [11]. A plethora of fabrication techniques and detection methods have been proposed, and are described in recent reviews [12], [13], [14].

While substantial advances have been made in μPAD development, the question remains whether they can replace traditional and well-established analytical methods commonly used for water analysis or are suitable for screening purposes only. Are they sufficiently sensitive and robust to be applied in the field? With these questions in mind, the present article aims to provide a critical review of μPADs that have been developed and applied to water analysis. Each μPAD will be highlighted in terms of its main features (e.g. fabrication and detections methods) and analytical figures of merit, along with an individual pictorial description. A critical assessment of their precision, accuracy and real-life applicability will also be the focus of this review.

Section snippets

Water analysis applications

Parameters, such as the concentrations of nutrients, heavy metals and organic contaminants (e.g. pesticides); microorganism count; pH; and dissolved oxygen content, amongst others, are commonly used to assess water quality. Each parameter provides essential information about some aspect of the nature or health of a particular water body or source. In addition to the numerous parameters that must be monitored, the nature and concentrations of the analytes in a water sample may vary significantly

Fabrication methods and design

The fabrication of µPADs is generally based on the creation of hydrophilic zones on paper, patterned by hydrophobic or physical barriers using different hydrophobic agents or cutting methods, respectively [12], [13]. The fabrication methods most commonly used to prepare the µPADs listed in Table 1, Table 2, Table 3, Table 4, because of their simplicity and cost-effectiveness, are wax or AKD printing as well as paper cutting. Other fabrication approaches involve modifying the filter paper by

Detection methods

This section outlines the detection methods used by the μPADs listed in Table 1, Table 2, Table 3, Table 4, namely colorimetric, luminescence, electrochemical, and photoelectrochemical detection. The fundamentals of these methods will be briefly described and their advantages and disadvantages will be discussed. Moreover, the possibility of multiplex detection and multi-parametric measurements will also be addressed.

Analytical performance and method validation

Any new analytical method must be validated to ensure that the method is reliable and that it can be applied by other analysts. In-house method validation usually includes evaluation of precision, limit of detection, linearity, selectivity, and accuracy [102], [103]. All of these, except for the selectivity and accuracy, are included in the “Analytical Figures of Merit” listed in Table 1, Table 2, Table 3, Table 4. It can be observed that precision, expressed as relative standard deviation

Applicability beyond proof of concept

Much of the interest in μPADs derives from their simple construction, low cost and suitability for on-site analysis. Ideally such a device should be “fit for purpose”, i.e. should be able to function effectively over a concentration range that covers the concentrations specified in water guidelines or legal limits, as well as those commonly found in the environment. Hence, in order to assess whether the μPADs covered by the present review can be realistically applied beyond their proof of

Portability and on-site analysis

Portability is one of the most important features of μPADs. By eliminating the need to transport samples to the laboratory, the risk of sample contamination or degradation is minimised, and the need for sample preservation is avoided. On-site analysis thus enables a faster response in terms of results at a lower cost of analysis. However, this is only possible if the detection method used is also portable and user-friendly. As noted in the Detection Methods section there are several options

Conclusions and future trends

On the basis of the critical assessment of the μPADs for water analysis, developed so far, it can be concluded that considerable progress has been achieved in the adaptation of existing batch and flow analysis methods to μPAD format. It appears that there are no real obstacles for this trend to continue unabated and to result in the development of μPADs for the detection of a wide variety of inorganic and organic analytes of environmental and health concern.

The most frequently used fabrication

Acknowledgements

The authors are grateful to the Australian Research Council (ARC) and Melbourne Water Corporation for financial support (ARC Linkage grants LP110200595 and LP160100687).

This paper is dedicated to Professor Gary Christian on the occasion of his 80th birthday (25 November 2017).

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