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30 protocols using mc lr

1

Microcystin-LR Production in Microcystis aeruginosa

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Microcystis aeruginosa (unicellular, LB 2385, UTEX Culture Collection of Algae at the University of Texas at Austin, hereafter “M. aeruginosa”) was confirmed to produce only microcystin-LR (MC-LR) and cultured as described in previous work [29 (link)]. After 30 days of culture growth, cells were centrifuged and rinsed with 1 mM phosphate buffer adjusted to pH 7.5 (hereafter, phosphate buffer) three times and ultimately suspended in phosphate buffer at concentrations of 1 × 105 cells/mL (low-density), 1 × 106 cells/mL (medium-density), and 1 × 107 cells/mL (high-density) for cell lysis experiments. The concentration of M. aeruginosa cells in the stock suspension was confirmed by counting cells using digital flow cytometry as described in previous work [30 (link)]. The cell densities corresponded with approximately 5, 20, and 40 µg/L total MC-LR, respectively (verified for each batch of cell suspension via analysis of a sample subjected to three freeze-thaw cycles).
Additionally, a known concentration of MC-LR (Enzo Life Sciences, ≥95%), ~15 µg/L, was spiked into phosphate buffer as a control solution to ensure cyanotoxin recovery.
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2

Microcystin Exposure Effects on Spirodela

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Separate tests were carried out for three MC variants (MC-RR, MC-LR, and MC-LF, Enzo Life Science, Lausen, Switzerland). Tap water sourced from underground intakes and filtered through a bacteriological filter (0.2 µm; Millipore, Cork, Ireland) was used as a medium both in controls and experimental variants containing S. polyrhiza. The tests were performed in three replicates in multi-well plates. MC-RR, MC-LR, and MC-LF were added respectively to each plate-well containing 2 mL of tap water to obtain the final concentration equal to 1000 ng/mL for each MC. The final concentration was controlled by HPLC analysis. Each three-week-old plant used in the experiments was randomly picked from the flask, gently rinsed three times with the experimental tap water, and placed into plates (one plant per one plate-well) containing MC-RR, MC-LR, and MC-LF, respectively. The plates were incubated in the cabinet for the following four and nine days at 20 °C with a light:dark cycle of 12:12 h (6000 lux). Controls with MCs and the tap water were set up in three replicates in a separate plate and incubated in the conditions described above.
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3

HPLC-Photodiode Array for Microcystin Analysis

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The HPLC-photodiode array detection system (Shimadzu, Kyoto, Japan) was used for the detection and identification of MCs and their degradation products. The UV detection range was 200–300 nm. MC-RR, MC-LR, and MC-LF (Enzo Life Science, Lausen, Switzerland) were used as the standards. Separation of supernatant components was performed using a Purosphere column (125 × 3 mm, dp 5 µm, Merck, Darmstadt, Germany) with the mobile phase composed of acetonitrile (Merck, Burlington, VT, USA) and gradient-grade water for HPLC acidified with 0.05% trifluoroacetic acid (gradient 30–100%), at a flow rate 0.7 mL/min. MCs and their biodegradation products were identified on the basis of specific spectra and the time of elution compared with the spectra and elution times of standards. Each fresh MC standard used in the experiment, to prepare a calibration curve, and to identify MCs and their degradation products had one specific peak and spectrum.
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4

Microcystin-LR Exposure and β-Catenin Inhibition

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The material used in this study was Microcystin-leucine arginine (MC-LR) (ALX-350-012-M001; Enzo Life Sciences, NY, USA). To prepare the concentrate solution, 1 mg of MC-LR was suspended in 1000 μL of dimethyl sulfoxide (DMSO), yielding a concentration of 1 mM. To obtain 1, 10, 100, and 1000 nM of MC-LR for each experiment, the concentrate solution was diluted with the completed DMEM medium. These concentrations of MC-LR for treatment groups were selected based on microcystin-polluted surface waters, typically below 100 μg/L (equivalent to approximately 100.5 nM) [29 (link)], as well as many previous studies [23 (link),[30] (link), [31] (link), [32] (link)] that have utilized this concentration range.
The β-catenin inhibitor, MSAB (HY-120697; MedChem Express, NJ, USA) was first diluted with DMSO to prepare the stock solution. For the working solution, the inhibitor was further diluted with completed DMEM medium to achieve a 10 μM of MSAB. The inhibitor was treated to the cultured cell 24 h before MC-LR treatment.
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5

Western Blot Analysis of OATP1B2 and MCLR

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Tissue lysates (20 µg/well) were prepared in Laemmli sample buffer with 2.5% BME and heated at 37 °C for 30 min. Protein was transferred from the gel to polyvinylidene fluoride (PVDF) membrane using the Trans-Blot Turbo Transfer System at 25 V and 1.0 A for 30 min. Following transfer, the membranes were imaged under UV to capture Stain-Free image used for protein normalization. The blots were then blocked with 5% non-fat dry milk in Tris-base buffered saline-Tween 20 (TBS-T) for 1 h at room temperature, then incubated with primary antibody overnight at 4 °C. Membranes were probed for OATP1B2 (1:1000 dilution; Santa Cruz Biotechnology, Santa Cruz, CA, USA, Cat. 376904) and MCLR (1:2000 dilution; Enzo, Farmingdale, NY, USA, Cat. 89154-022). The blots were incubated with secondary antibody in 5% non-fat dry milk in TBS-T for 1 h at room temperature. Densitometry was performed using Image Lab (Bio-Rad, Standard Edition, Version 6.0.0 build 25). Proteins of interest were normalized to total protein as captured by Stain-Free image. Total protein normalization is a commonly accepted technique for protein densitometry analysis instead of the single-protein loading control [101 (link)].
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6

Standardized Microcystin Quantification

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Inorganic chemicals and organic solvents were reagent grade or better. Standard of MC-LR for the multihapten-ELISA were from Enzo Life Sciences Inc. (Farmingdale, NY, USA), and this was in-house calibrated against a CRM-MCLR from NRC (Halifax, NS, Canada). The standard for the Adda-ELISA was as provided with the kit (Abraxis LLC, Warminister, PA, USA).
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7

Chronic MC-LR Exposure in Mice

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SPF male APCmin/+ C57BL/6 mice (aged 6–7 weeks, 20–22 g) were obtained from GemPharmatech Co., Ltd. (Nanjing, China) and maintained at the Animal Core Facility of Nanjing Medical University. The mice were nourished with a standard rodent diet and maintained in a controlled environment with a 12:12 h light–dark cycle. After adapting to the environment for 2 weeks, 24 mice were randomly and equally assigned to two groups: a treatment group (gavage with 40 µg/kg MC-LR dissolved in 0.9% NaCl solution) and a control group (gavage with the same 0.9% NaCl solution based on mice body weight). MC-LR, with a purity exceeding 95%, was procured from Enzo Life Sciences (Farmingdale, NY, USA). The mice received either the 0.9% NaCl solution or MC-LR by oral gavage for 8 weeks. Body weights were measured daily.
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8

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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9

Analytical Protocols for Cyanotoxin Determination

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Gibco (Biomol, Sevilla, Spain) has provided the fetal bovine serum (FBS), minimum essential medium (MEM) and cell culture reagents. HPLC-grade methanol, dichloromethane, trifluoroacetic acid (TFA) and formic acid were obtained from Merck (Darmstadt, Germany). Deionized water (>18 MΩcm-1 resistivity) was obtained from a Milli-Q water purification system (Millipore, Bedford, MA, USA). The MTS (3-(4,5- dimethylthiazol-2-yl)-5-(3-carboxymethoxyphenyl)-2-(4-sulphophenyl)-2H-tetrazolium salt) Cell Titer 96® AQueous One Solution Cell Proliferation Assay was purchased in Promega (Biotech Iberica, Madrid, Spain). The neutral red (NR) and the Bradford reagent were obtained from Sigma-Aldrich (Madrid, Spain). BOND ELUT® Carbon cartridges (500 mg, 6 mL) were supplied by Agilent Technologies (Amstelveen, The Netherlands, Europe). CYN (95%), (+/−) ATX, MC-LR, MC-RR and MC-YR (99%) standards were supplied by Enzo Life Sciences (Lausen, Switzerland).
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10

HT-29 Cell Culture and MC-LR Exposure

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HT-29 cells were obtained from the American Type Culture Collection (Manassas, VA, USA) and maintained in a monolayer culture in Dulbecco's modified Eagle's medium (DMEM; Hyclone; GE Healthcare Life Sciences, Logan, UT, USA), containing 100 µg/ml streptomycin, 100 µg/ml penicillin and 10% fetal bovine serum (FBS; Hyclone; GE Healthcare Life Sciences). Cells were cultured in a humidified atmosphere of 5% CO2 at 37°C. HT-29 cell culture was performed according to the manufacturer's protocol and as previously described by Miao et al (18 (link)). MC-LR (Enzo Life Sciences, Inc., Farmingdale, NY, USA) was dissolved in sterile water to make a 0.25 nM stock solution and then added in the medium to reach different doses (0, 1, 5, 12.5, 25 and 50 nM).
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