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13 protocols using model 515

1

HPLC Assay for Drug Quantification

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The apparatus used was a Waters HPLC system model 746 (Milford, US), consisting of a model 515 intelligent solvent delivery pump, a 100 μl injection loop, a computerized system controller, and a Waters 2487 UV detector. HPLC assay was carried out on a μ-Bondapack C18 column (250 mm × 4.6 mm, 10 μm, Waters, Ireland). The mobile phase consisted of potassium dihydrogen phosphate (0.1 M)/acetonitrile at 80/20 (pH, 3 ± 0.1) eluted at flow rate 1.5 ml/min. Column effluent was detected at 276 nm with a UV detector. Column temperature was set at 40°C, and 50 µl of samples was injected to the HPLC system.
Quantitation was achieved by measurement of the peak area ratios of the drug to the IS.
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2

Pressurized Liquid Extraction of Samples

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The PLE assays were carried out in an extraction unit developed at LATESC and minutely described by Gonçalves Rodrigues et al (2019) (link).
First, 5 g of sample was inserted into the 90 mL extraction vessel and its void fraction was filled with cotton layers and glass beads. Following this, the solvent was delivered to the system by an HPLC pump (Waters, Model 515, Milford, MA, USA), passed through a pre-heating vessel to reach the target temperature, and then flowed downstream through the extraction vessel. Once the extraction pressure of 100 bar was reached, the needle valve was opened and the extraction began in a continuous mode. During the extraction process, 100 mL of solvent were used, maintaining the same 1:20 w/v solute to solvent ratio used for MAE. The specific PLE variables can be seen in section 2.7.
Finally, the extracts were submitted to rotary evaporation and stored in amber flasks at −18 °C until further analysis.
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3

HPLC Analysis of Compound Mixtures

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Waters HPLC (Milford, MA, USA) system used was equipped with a binary gradient pump (Model 515, Waters), an autosampler injector (Model 2707, Waters) and a diode array detector (Model 2998, Waters). Waters HPLC interface and Empower software by Waters corporation, USA was utilized for data acquisition. The analytical column RP-18e B Lichrosphere® (250 mm × 4 mm, 5 μm, Merck, Germany) at 30°C ± 3°C was used for the study. The mobile phase included ACN water (70:30, v/v) and was degassed before analysis using a Millipore vacuum pump. Column effluent was monitored at 220 nm and 254 nm (photodiode array detection) with a total runtime of 30 min. The flow rate was maintained 1.0 ml/min. and injection volume remained 20 μL.
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4

Characterization of High-G/M and Mid-G/M Alginates

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Sodium alginate with molecular weight (Mw) of 520 kDa and G/M ratio of 64/36 was designated High-G/M alginate, and sodium alginate with Mw of 532 kDa and G/M ratio of 34/66 was designated Mid-G/M alginate. Both were purchased from Qingdao Mingyue Seaweed Group Co., Ltd. (Qingdao, China). The detailed information of both purchased alginates was characterized by GPC and 1HNMR spectroscopy (Table 1).
The G/M ratio of the respective alginates was determined at 80°C by 1HNMR spectroscopy using an AVANCE NB-360 spectrometer (Bruker, Germany). The Mw and molecular weight distribution (Mw/Mn) of alginate samples were analyzed via gel permeation chromatography (GPC) using a system equipped with two TSK-gel size-exclusion columns (G4000PWXL and G3000PWXL), a refractive index detector (Waters, model 2414, Milford, MA), and an HPLC pump (Waters, model 515).
Collagen, acquired from rat tails, and was obtained by our laboratory. Anhydrous calcium chloride (CaCl2) was purchased from Sigma-Aldrich (Merck Life Science (Shanghai) Co., Ltd.). All other chemical reagents were analytical grade and used as received.
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5

HPLC Analysis of Withanolide A

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chromatographic conditions: The Waters HPLC (Milford, MA, USA) system used was equipped with a binary gradient pump (model 515, Waters), an autosampler injector (Model 2707, Waters), and a diode array detector (Model 2998, Waters). The Waters HPLC interface and Empower 2 software were utilized for data acquisition. The HPLC resolution of Withanolide A was achieved on an RP-18e Lichrosphere® column (250 × 4 mm, 5 μm, Merck, Germany) at 30 ± 3°C utilizing the mobile phase consisting of acetonitrile: Water (1:1); flow rate of 1.0 mL/minute, and injection volume that remained at 20 μL. The column effluent was monitored at 240 nm (PDA detection).
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6

HPLC Analysis with Multidetector Setup

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A Waters HPLC system consisted of an isocratic pump (Model 515), an autosampler (Model 710 plus) and a variable UV-Vis detector (Model 480) was used. A multi-channel Chrom & Spec software for chromatography, version 1.5 x was used for data processing. A dry air oven (Melag, Germany) was used for heating the samples. The light sources were a l00 W Tungsten lamp (visible light) and a low-pressure Mercury lamp 200 W (UV light) with λmax around 254 nm.
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7

Fluorescent Particle Microscopy Analysis

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Fluorescent polystyrene particles (0.79, 0.92 and 1.0 µm, Thermo Scientific Fluoro-Max) were suspended in deionized water (with 0.1% of Triton X to reduce agglomeration) in a concentration of ∼ 0.001 vol%.
An HPLC pump (Waters, model 515) was used to pump the samples through the devices at a controlled flow rate with a read out of the pressure.
During the operation, the devices were observed with an inverted fluorescence microscope (Olympus IX73 with an Orca-Flash 4.0 LT digital CMOS camera). Images were taken with a magnification of 20X and a 2 s exposure time.
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8

HPLC Analysis of Organic Compounds

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The apparatus used was a Waters HPLC system model 746 (Milford, US) consisting of a model 515 intelligent solvent delivery pump, a 100-μL injection loop, a computerized system controller, and a Waters 2487 UV detector. Chromatographic separation was achieved using a μ-Bondapak C18 column (3.9 mm × 250 mm Waters, Ireland). The mobile phase consisted of water/acetonitrile at 60/40 eluted at a flow rate of 1.2 mL/min. Column effluent was detected at 230 nm with a UV detector.
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9

HPLC Analysis of Thermal and Photolytic Degradation

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The HPLC system consisted of a pump (Model 515), a UV-Vis detector (Model 486), and an autosampler (Model 717) from Waters (Milford, USA). The HPLC data were processed using multi-channel Chrom&Spec software, version 1.5 x. Thermal degradation was performed in a Melag dry air oven (Germany). A 100 W tungsten (visible light) and a low pressure mercury lamp (UV light) were used for the photolytic degradation studies.
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10

HPLC Analysis of Acetate Buffer Compounds

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The apparatus used was a Waters HPLC system model 746 (Milford, US) consisting of a model 515 intelligent solvent delivery pump, a 100 μl injection loop, a computerized system controller, and a Waters 2487 UV detector. Chromatographic separation was achieved using a µ-Bondapak C 18 column (3.9 mm × 250 mm Waters, Ireland) heated at 58 • C. The mobile phase consisted of acetate buffer (0.01 M)/ acetonitrile at 58/42 (pH, 5 ± 0.1) eluted at flow rate 1.9 ml/min. Column effluent was detected at 227 nm with a UV detector.
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