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12 protocols using mc la

1

Microcystin Toxin Analysis in Water Samples

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In triplicate, 200 mL of water sample was filtered (CFC, Whatman, Maidstone, UK), filter papers were wrapped individually in aluminium foil and preserved at −80 °C. On analysis, filter papers were subjected to three cycles of freeze-thawing before submersion in 10 mL of 80% aqueous methanol. Samples were left in the dark at 4–6 °C for 24 h, before ~0.5 mL was aliquoted into a LCMS certified vial. Toxin analysis was carried by ultra-high-performance liquid chromatography (UHPLC) (Acquity, Waters, Manchester, UK) coupled to a tandem quadruple mass spectrometer (Xevo TQ, Waters, Manchester, UK). All instrument solvents and chemicals were of LC-MS-grade (Fisher Optima, Thermo Fisher, Manchester, UK). Reference toxins used for the detection method included the microcystin analogues MC-RR, MC-LA, MC-LY, MC-LF, MC-LW, MC-YR, MC-WR, MC-HilR, MC-HtyR, MC-LR & Asp3-MC-LR (Enzo Life Sciences, Exeter, UK) and [Dha7]-MC-LR and matrix reference material of blue-green algae (RM-BGA, Lot 201301) containing a range of microcystins (Institute of Biotoxin Metrology, National Research Council Canada). Analysis of microcystins was conducted following the method by Turner et al. [50 (link)].
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2

Quantitative Analysis of Cyanotoxin Standards

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Mobile phases were prepared from LC-MS-grade acetonitrile (Fisher Optima, ThermoFisher, Greater London, UK) and water used for LC-MS was obtained in-house. Sample preparation reagents were HPLC grade. Toxin standards used for preparation of calibration solutions (MC-RR, MC-LA, MC-LY, MC-LF, MC-LW, MC-YR, MC-WR, MC-HilR, MC-HtyR, MC-LR, [Asp3] MC-LR and Nodularin) were all obtained from Enzo Life Sciences, Exeter, UK. A certified standard of [Dha7] MC-LR was obtained from the Institute of Biotoxin Metrology, National Research Council Canada (NRCC, Halifax, NS, Canada). Reference standards received as solid films were dissolved in 50% aqueous methanol, to form stock solutions. A mixed stock solution was subsequently prepared by combining aliquots of each stock, followed by further dilutions to create seven-level suite of working calibration standards between 0.33 ng/mL to 327 ng/mL per toxin.
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3

Quantitative Analysis of Cyanotoxins

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MCs (MC-LR, MC-YR, MC-RR, MC-LA, MC-LY and MC-LF) and NOD standards were purchased from Enzo Life Sciences, Ltd. (UK), CYN was obtained from n’Tox (France) and ATX-A was purchased from the National Research Council, Canada. MMPB was purchased from Wako Pure Chemical Industries, Ltd. (Japan). CYN N15-labelled internal standard (N14 → N15) was a gift from the Federal Institute for Materials Research and Testing (BAM), Berlin, Germany. Acetonitrile and methanol, LC-MS Chromasolv grade, dichloromethane, formic acid, trifluoroacetic acid, potassium permanganate, sodium (meta) periodate and sodium bisulfite were all purchased from Sigma-Aldrich, UK, as were the ENVI-Carb solid-phase extraction (SPE) cartridges (250 mg, 3 cm3). Oasis HLB and PRiME SPE cartridges (60 mg, 3 cm3) were purchased from Waters, Ireland. The water used was supplied from an in-house Milli-Q water system (Millipore, Ltd., UK), with conductivity and total organic content (TOC) of the water being 18 MΩ and 3 ppb, respectively.
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4

Extraction and Preparation of Cyanotoxin Standards

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The solvents for the extraction and for the basis of the mobile phase were UHPLC-MS grade. All toxin standards for MCs (MC-LR, MC-RR, MC-LA, MC-LY, MC-LF, MC-LW, MC-YR, MC-WR) and NOD came from Enzo Life Sciences® (Antwerp, Belgium) and were received under the form of a solid powder. After dilution in 100% methanol (MeOH), mixed stock solutions were prepared in 50% methanol (MeOH) (50% Milli-Q water with 1% acetic acid (v/v)). The stock and the intermediate solutions were stored at −20 °C.
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5

Comprehensive Microcystin Quantification

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LC-MS grade acetonitrile, water and formic acid and HPLC-grade methanol and water were purchased from Fisher (ThermoFisher, UK). Reference toxin standards of microcystins (MC-LR, MC-RR, MC-YR, MC-WR, MC-LW, MC-LA, MC-LY, MC-LF, MC-HtyR, MC-HiLR, [Asp3]-MC-LR/[Dha7]-MC-LR) and NOD ≥95% were as per Enzo Life Sciences (Exeter, UK) (Fig. S1). A certified standard of [Dha7]-MC-LR and a pre-certified freeze-dried matrix reference material of blue-green algae (RM-BGA, Lot 201301) containing a range of MCs were purchased from the Institute of Biotoxin Metrology, National Research Council Canada (Ontario, Canada).
A mixed stock solution was prepared by combining aliquots of each toxin to give a final concentration of 327 μg/L. For external calibration, a seven point calibration curve was prepared by serial dilution with methanol/water (1:1, v/v) in the range of 0.33–327 μg/L for each toxin and stored at – 18 °C. A quality control reference material (RM-BGA, National Research Council, Halifax, Canada) was prepared, with toxins extracted in the supernatant after 28 mL of methanol/water (1:1, v/v) + 0.1% acetic acid were added to RM-BGA (280 mg) and subsequent centrifugation (4500  × g; 10 min).
Shellfish diet 1800 (approximately 7.4 × 1011 cells/mL) was purchased from ReedMariculture Inc., (US) and dilutions were made in water/seawater (10:0.86, v/v).
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6

Comprehensive Cyanotoxin Analysis in Water

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We measured toxins in 246 whole-water samples spanning 6 y (2013 to 2018). These samples were taken from the same water grabs used to characterize the microbial community. We quantified cyanotoxins using methods described in detail by Miller et al. (16 (link)). Briefly, lyophilized samples were resuspended in formic acid, subjected to three freeze-thaw cycles, and extracted in methanol and formic acid in a sonicating water bath. The extract supernatant was analyzed by targeted high-performance liquid chromatography coupled with tandem mass spectrometry (HPLC-MS/MS).
Eleven microcystin (MC) congeners and three anabaenopeptin (Apt) congeners were analyzed. Certified reference standards of MC-LR, [Dha7]MC-LR and nodularin were purchased from the National Research Council of Canada Biotoxins program (Halifax, Nova Scotia). MC-LA, MC-RR, MC-LF, MC-YR, MC-WR, MC-LY, MC-LW, MC-HtyR, and MC-HilR (all >95%) were purchased from Enzo Life Sciences (Farmingdale, NY). Anabaenopeptin A (Apt-A) (>95%), Apt-B (>95%), and Apt-F (>95%) were purchased from MARBIONC (Wilmington, NC). To calculate total concentrations, we summed nanomolar measurements of the congeners. 99 ± 4% of total microcystin was comprised of the congeners MC-LA and MC-LR. Toxin totals are available in a tabular format as Dataset S1.
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7

Quantitative Analysis of Cyanotoxins

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Microcystin reference standards for MC-LR, MC-YR, MC-RR, MC-LF, MC-LA, MC-LW, MC-LY, and Nodularin were obtained from Enzo Life Science (Lausen, Switzerland). Cyanopeptolin A, cyanopeptolin D, anabaenopeptin A, anabaenopeptin NZ857, and oscillamide Y were obtained as bioreagents from CyanoBiotech GmbH (Berlin, Germany). Aerucyclamide A was obtained as a purified bioreagent in dimethyl sulfoxide by Prof. Karl Gademann (University Zurich, Switzerland). (37) Additional materials are listed in the Supporting Information.
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8

Cyanotoxin Standard Preparation Protocol

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CYN, ANA, MC-LR, MC-RR, MC-YR, MC-LY, MC-LW, and MC-LF (99%) standards were purchased from Cyano Biotech GmbH (Berlin, Germany). NOD and MC-LA were purchased from ENZO life Science (Lausen, Switzerland). Methanol (MeOH), acetonitrile (ACN), and water HPLC grade were obtained from Fisher Scientific (Leics, UK). FA (98%) was purchased from Fluka (Steinheim, Germany). NH4OH (25%) was obtained from Sigma-Aldrich (Steinheim, Germany). Sodium chloride, potassium chloride (99.5%), and sodium carbonate (99.9%) were purchased from Merck (Darmstadt, Germany). Calcium chloride (93%), magnesium chloride (98%), and HEPES (99.5%) were obtained from Sigma-Aldrich (Steinheim, Germany). AFW was prepared according to Lipschitz et al. [44 (link)], and Na2CO3 1M was used for AFW pH adjustment
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9

Microcystin Identification and Quantification

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The extracts were separated using a Purospher STAR RP-18 end-capped column (30 × 4 mm, 3 μm particle size, Merck, Darmstadt, Germany) at 30 °C as described by Spoof et al. [62 (link)]. The mobile phase consisted of 0.5% formic acid (A) and acetonitrile with 0.5% formic acid (B) at a flow rate of 0.5 mL/min with the following gradient program: 0 min 25% B, 10 min 70% B, 11 min 70% B. The injection volume was 10 μL. Identification and quantification of the MCs ([Asp3]-MC-RR, MC-RR, MC-YR, [Asp3]-MC-LR, MC-LR, MC-LW, MC-LF, MC-LA, standards purchased at Enzo Life Sciences, Lörrach, Germany) was performed in the MRM (Multiple Reaction Monitoring) mode with the transitions given by Fastner et al. [63 (link)].
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10

Cyanotoxin Analysis with Mass Spectrometry

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Instrument solvents used for preparation of mobile phases were of LC-MS-grade (Fisher Optima, ThermoFisher, London, UK) and all chemicals were LC-MS reagent grade where possible, otherwise HPLC grade. Sample preparation reagents were all HPLC grade. Cyanotoxin reference toxin standards comprising the microcystin analogues (MC-RR, MC-LA, MC-LY, MC-LF, MC-LW, MC-YR, MC-WR, MC-HilR, MC-HtyR, MC-LR, [Asp3] MC-LR), Nodularin (Nod), ATX, Cylindrospermopsin (CYN) were all obtained from Enzo Life Sciences (Enzo, Exeter, UK), with secondary calibration check standards and Saxitoxin (STX) standard prepared using certified reference solutions from Biotoxin Metrology, National Research Council of Canada (NRCC, Halifax, Nova Scotia, Canada). Enzo reference standards received as solid powders were dissolved in suitable volumes of 50% aqueous methanol, to form stock solutions. A mixed stock solution was prepared by combining aliquots of each stock, followed by a seven-level suite of working calibration solvent standards resulting in a calibration range between 1.0 ng/mL to 500 ng/m per toxin. Phe was also obtained from Merck (Poole, UK) and used for confirmation of resolution from ATX, given the isobaric nature of the two compounds and the potential for false positive detection of ATX in matrices containing Phe [62 (link)].
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