Selective and easy detection of microcystin-LR in freshwater using a bioactivated sensor based on multiwalled carbon nanotubes on filter paper
Introduction
Cyanobacterial outbreaks occur in surface water bodies as a result of eutrophication and warm weather. Cyanobacteria release a group of toxins known as microcystins (MCs) (Greer et al., 2018; USEPA, 2015). Of these, microcystin-LR (MC-LR) is a cyclic heptapeptide that consists of five non-proteinogenic amino acids and leucine (L) and arginine (R) residues at the two and four positions. MC-LR is the most toxic congener of the MCs, having a median lethal dose (LD50) of 43 μg/kg (Alosman et al., 2020). The World Health Organization (WHO) stipulates that the level of MC-LR in drinking water should be less than or equal to 1 ng/mL (WHO, 2003).
Currently, the MC-LR concentration in contaminated water is determined by high-performance liquid chromatography and tandem mass spectrometry (LC/MS/MS) (Draper et al., 2013; Picardo et al., 2019; Roy-Lachapelle et al., 2019). However, this technique cannot be carried out at sites of pollution because it requires sophisticated instruments. In addition, LC/MS/MS analysis involves high running costs ($50/sample in Korea) and is time-consuming. Several alternative MC-LR quantification methods have been reported but still require much improvement for practical applications (Picardo et al., 2019).
As part of the efforts to develop better biosensors (Li et al., 2019; Aliakbarinodehi et al., 2016; Taghdisi et al., 2017), carbon nanotube (CNT)-based biological sensing systems have been used. CNTs have attracted research interests as active elements for biosensors because of their high aspect ratio, large surface area, good electrical conductivity, and high chemical stability (Yola et al., 2021). In these sensors, detection is based on electrochemical methods. Examples include ionic liquid-CNT-modified electrodes (Aliakbarinodehi et al., 2016), electrochemiluminescent systems containing CNTs (Taghdisi et al., 2017), and electronic methods based on CNT field-effect transistors (FET), for which the latter has reached an MC-LR detection limit of approximately 0.6 ng/L (Tan et al., 2015). Nevertheless, these biosensors still have several disadvantages, including high cost, complexity, and the need for laboratory-based experiments.
A few years ago, our group reported (Ji et al., 2018) that bioactivated multi-wall carbon nanotubes (MWCNTs) deposited on a micropore filter paper could be used to detect prostate-specific antigen (PSA) at diagnostic levels (detection limit: 1.18 ng/mL) within 2 h. The detection mechanism of the MWCNT sensor is based on the change in the potential barrier between the p-type conducting filaments (MWCNTs) induced by the interaction between the target molecule (PSA) and active site (PSA antibody) attached to the MWCNTs. However, the drawback of this paper-based sensor is the lack of repeatability, which is mainly due to the uneven deposition of the MWCNTs on the filter paper and the instability of the attached PSA antibody. Specifically, the sensor could not be dried after the bioactivation process because the PSA antibody lost its activity, and the production yield was only around 30 %. Therefore, improvements in these paper-based sensors should be made to enable their practical application. Jin et al. reported (Jin et al., 2020) a sensor that allowed the diagnosis of early-stage pancreatic cancer by detecting CA19-9, a biomarker of this disease, using an improved device to detect the paper-based sensor. Their sensor could also be stored for up to 7 days by using a freeze-drying method.
Aptamers are synthetic single-stranded antibody-like DNA or RNA molecules that bind selectively to their target biomolecules (Aliakbarinodehi et al., 2017; Odeh et al., 2020). For the detection of target proteins, aptamers have significant advantages over antibody-based approaches, including easy synthesis, easy chemical modification, high stability, and reversible denaturation (Morales et al., 2018); most importantly, the activity of the dried aptamer is fully recovered upon re-wetting (Liu et al., 2011). In a recent report (Cunha et al., 2018), the MC-LR targeting aptamer (MCTA: DNA oligonucleotide 5-NH2-C6-AN6) was selected from random libraries of synthetic DNA/RNA sequences using a SELEX selection procedure.
In this study, we present a reliable paper-based aptasensor for the label-free detection of MC-LR in freshwater. The immobilization of MCTA on MWCNTs achieved high sensitivity and specificity, and the MCTA-modified MWCNTs were evenly deposited on the micropore filter paper by suction filtering. We tested the produced biosensor for its detection sensitivity and selectivity under the matrix effect conditions related to the ions present in freshwater samples. The demonstrated strategy provides an inexpensive tool for the fast analysis of MC-LR in environmental samples at remote sites of undeveloped countries.
Section snippets
Experimental
Nitric acid (64.0–65.0 %) was purchased from Duksan Science (Ansan, Korea). CaSO4 (>99%), NaCl (>99.9 %) were purchased from Junsei Chemical Co., LTD. (Tokyo, Japan), Al2O3 (300 nm in diameter) was purchased from Buchler (Lake Bluff, IL, USA). Phosphate-buffered saline (PBS, pH 7.2) was purchased from Biosesang Inc. (Seongnam, Korea). 2-(N-Morpholino) ethanesulfonic acid (MES, 1 M, pH = 5.0) and 0.05 % Tween 20 + 1 % bovine serum albumin (BSA) in PBS were purchased from Tech & Innovation
Sensor preparation
Fig. 1 shows the FT-IR spectra of (a) pristine, (b) carboxylated, (c) MCTA-activated, and (d) BSA-coated MCTA-activated MWCNTs (MCTA-MWCNTs). Absorption bands are assigned as marked in the figure. The spectrum in Fig. 1(b) indicates that the carboxylation of MWCNTs with c-HNO3 had successfully generated –COOH groups. In the next step, the MCTA was immobilized on the MWCNTs by amide coupling between the amine group (–NH2) in MCTA and the carboxyl group (-COOH) in MWCNTs. Therefore, the intensity
Conclusion
MCTA-modified MWCNTs on filter paper were prepared to detect MC-LR. The biosensor could easily detect MC-LR from 0 to 2.0 ng/mL in freshwater samples within 1.5 h without the need for expensive and sophisticated instrumentation. In particular, the sensor had a very low detection limit (0.19 ng/mL) between 0 and 0.5 ng/mL MC-LR. In addition, the sensor showed good selectivity for MC-LR in the presence of similar MC congeners and high sensitivity, enabling the detection of MR-LR within the WHO
CRediT authorship contribution statement
Myeongsoon Lee: Investigation, Data curation, Visualization, Writing – original draft. Hak Jun Kim: Conceptualization, Resources. Don Kim: Supervision, Writing – review & editing, Investigation.
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
This study was supported by the Basic Science Research Program through the National Research Foundation of Korea (NRF) funded by the Ministry of Education (NRF-2019R111A3A01061858).
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