Rapid, multiplex-tandem PCR assay for automated detection and differentiation of toxigenic cyanobacterial blooms
Introduction
Cyanobacteria (‘blue–green algae’) are amongst the oldest, most abundant and widely distributed forms of life on the planet. These bacteria provide a basis for many of the world's aquatic ecosystems [1], and are one of the world's major carbon-sinks and oxygen producers [2]. However, in drinking or recreational waters, particularly during warmer months of the year, high-density cyanobacterial populations (i.e., blooms) may represent a significant threat to water quality and/or environmental health [3], can illicit allergic dermatitis [4], [5] and affect taste/palatability of the water [6]. Most significantly, many cyanobacteria species produce small molecules, including cyclic peptides [e.g., nodularins (NODs) and microcystins (MCYs)] and alkaloids [e.g., cylindrospermopsins (CYNs) and paralytic shellfish toxins (PSTs), such as, saxitoxin (SXTs)], that are potent neuro-, cyto- and/or hepatotoxins in vertebrates and represent a significant risk to animal and public health [3], [7], [8].
Currently, a range of methods exist for the detection of toxic cyanobacteria in water. These include immunological, microscopical and DNA-based approaches. Various immunoassays allow the direct detection of cyanotoxins in water samples [9]; however, although often easy to use, such methods have limitations, both with respect to sensitivity (false-negatives) and specificity (cross-reactivity and false-positives) [10]. Although more sensitive and specific chromatography and mass spectrometry approaches are available [9], they can be costly and time-consuming for routine use. The primary tool used to determine the level of risk for cyanotoxin production is routine water surveillance and the identification of potentially toxigenic cyanobacterial species by light microscopy [11]. Although this allows taxonomic identification, toxigenicity cannot be assessed based on morphological observation alone [12].
The ability to produce cyanotoxins has been demonstrated to relate to specific biosynthetic pathways encoded by complex gene operons, which have been characterized for the major toxins [13]. Various PCR assays have been developed to detect toxigenic cyanobacterial blooms [13], [14], [15]. The advantage of these approaches is that they are low-cost and highly sensitive, and when coupled to mutation scanning tools and/or direct DNA sequencing, can allow assessment of the toxigenic potential of a cyanobacterial bloom. A limitation is that numerous, highly distinct toxigenic species can occur in the same geographical region or bloom [16], [17], [18]. Therefore, samples must be assessed using multiple distinct PCR assays, often using different cycling conditions. Multiplexed PCR, wherein multiple primer pairs are used to target and amplify distinct loci simultaneously in a single reaction, has been pursued as a method to improve the efficiency of PCR-based detection of toxigenic cyanobacteria [18], [19], [20]. Although effective, competition among primer pairs in multiplexed reactions often presents a significant technical challenge and differentiation/quantification of each amplicon relies on the use of target-specific (e.g., Taqman) probes, each labelled with a distinct fluorochrome, and, thus, multi-channel thermocyclers increasing the costs of such methods. Furthermore, each of the multiplex-PCR assays currently available for toxigenic cyanobacteria targets a subset of taxa/toxin producers [19], [20], [21], and each has distinct running conditions. Their combination into a single assay has not yet been achieved.
Multiplexed-tandem PCR (MT-PCR) overcomes many of the limitations associated with standard PCR diagnostic methods [21]. This approach uses a primary ‘target enrichment’ phase, consisting of a 10–20 PCR cycles conducted in multiplex, followed by a parallelized analytical amplification phase, with nested primer pairs specific to each assay run in tandem. Because the multiplexed stage of the PCR is terminated prior to exponential amplification, competition among primer sets is minimized and quantitative capacity is maintained [22]. When coupled to a final melting-curve analysis, the entire process is conducted remotely using a liquid handling robot and real-time PCR thermocycler, allowing semi-automated processing and detection, identification and quantification in a single channel thermocycler using a standard fluorogenic dye (e.g., SYTO-9) [22]. In the present study, we assessed an MT-PCR assay for the rapid, automated detection of toxigenic cyanobacteria from blooms able to produce each of the major known classes of cyanotoxins (MCYs, NODs, CYNs and/or PSTs), and established its diagnostic sensitivity and specificity relative to conventional PCR and direct toxin detection.
Section snippets
Sample collection and preparation
In total, 206 samples representing natural cyanobacterial bloom events and/or routine monitoring were collected as 1 l surface-water ‘grabs’ from fresh and/or estuarine waters representing recreational sources across Victoria (n = 185) and Queensland (n = 21), Australia, from September 2010 to August 2012. A ‘bloom event’ was defined as an occurrence where cyanobacterial volume exceeded an estimated 10 mm3/l (∼1000 cells/ml) based on phycocyanin-specific fluorescence [23], [24]. In addition, we
Assessment of MT-PCR specificity, sensitivity and quantitative potential
During the initial assessment of each MT-PCR assay, we determined the detection sensitivity and specificity of each assay against characterized toxigenic and non-toxigenic cyanobacteria cultures (see Table 1). In addition, each assay was tested against a panel of genomic DNAs representing common non-cyanobacterial microorganisms common to aquatic ecosystems (see Table 1). All positive controls were shown to amplify as expected, and the sequencing of each amplicon from each assay demonstrated
Discussion
In the present study, we developed an MT-PCR based assay for the rapid, semi-automated and simultaneous detection of toxigenic cyanobacteria blooms associated with the potential to produce MCYs, NODs, PST/SXTs and CYNs and critically evaluated this platform against existing conventional PCR protocols and direct detection of these toxins in water samples using commercially available immunodiagnostic methods. Evaluation of these assays against characterized control material representing known
Acknowledgements
We gratefully acknowledge funding for the current project from Water Quality Research Australia (WQRA), and thank the following Victorian water industry partners for their financial contributions and provision of field samples for testing: Barwon Water, Southern Rural Water, South Gippsland Water, Goulburn Murray Water, Goulburn Valley Water, Grampians Water, Melbourne Water Corporation, South East Water Limited and Western Water. We are also grateful to Susie Wood (Cawthron Institute, New
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2019, TrAC - Trends in Analytical ChemistryCitation Excerpt :In the same way, biotoxins of the main groups of cyanotoxins such as microcystins (MCs) and their congeners, nodularin (NOD), saxitoxin (STX), anatoxin-a (ANA-a), and cylindrospermopsin (CYN) can be detected by molecular methods through the detection of the genes present in the gene clusters encoding these biosynthetic enzymes [67,68]. For example, toxin genes such as cyrJ, sxtA, mcyE, ndaF correlate to the production of a toxin or toxin group as CYN, paralytic shellfish toxins, cricystis and NOD [69], respectively. Different multiplexed PCR assays have been as well developed for different groups of cyanobacteria such as MCs [70], and the single-plex PCR assays for STX [67] and ANA-a [68].
An improved method for PCR-based detection and routine monitoring of geosmin-producing cyanobacterial blooms
2018, Water ResearchCitation Excerpt :Based on our results, this new geoA PCR is a suitable, single protocol, tool for broad detection of the major geosmin-producing cyanobacteria. Given the small size of the novel geo799/927 amplicon developed herein (<130bp) and its consistency across numerous taxa, the current primer set is likely to support development of a geoA-targeted quantitative PCR (qPCR), as has been developed recently for a number of cyanotoxin biosynthetic genes (Baker et al., 2013). A geoA-targeted qPCR, would have significant utility in understanding the abundance of geosmin-producing cyanobacteria in a bloom, and their spatial and temporal distribution as well as providing a basis for exploring variability in geoA gene expression patterns, yielding insights into the function and timing of geosmin synthesis (Giglio et al., 2008, 2011; Su et al., 2013; Tsao et al., 2014; Watson et al., 2016).
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2017, Water ResearchCitation Excerpt :DNA was subsequently diluted 10- and 100-fold in TE buffer (10 mM Tris, 1 mM EDTA, pH 8) and then analysed using the GenePlex System (AusDiagnostics, Sydney), a multiplex tandem real-time PCR (Polymerase Chain reaction). The Cyano EasyPlex kit (Baker et al., 2013) was used to detect four toxin genes (cyrJ, sxtA, mcyE, ndaF) each one correlated to the production of a single toxin/toxin group (respectively CYNs, PSTs, MCYSTs and NOD) and the cyanobacteria-specific 16S rRNA gene, an internal control to confirm the presence of cyanobacterial DNA. An inbuilt internal control comprising synthetic DNA was used to determine whether there were PCR inhibitors in the DNA extracted from water samples.
A review of monitoring technologies for real-time management of cyanobacteria: Recent advances and future direction
2016, TrAC - Trends in Analytical ChemistryCitation Excerpt :For example, the microscopic enumeration method cannot provide in situ results and requires highly qualified personnel, while change in cell biovolume due to preservation by Lugol's Iodine solution can introduce measurement bias [21,28]. Real time qPCR is a promising technique but again requires skilled personnel and is not yet available as an “off the shelf” technology [29–31]. In contrast, currently available fluorometric probes (also called “fluorescence probes” in some publications) can theoretically provide an in situ estimation of cyanobacteria cell density.