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Oasis hlb 200 mg

Manufactured by Waters Corporation
Sourced in Switzerland, United States

The Oasis HLB 200 mg is a solid-phase extraction (SPE) cartridge designed for sample preparation. It utilizes hydrophilic-lipophilic balanced (HLB) sorbent to extract a wide range of analytes from various sample matrices.

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4 protocols using oasis hlb 200 mg

1

Quantifying Antibiotic Residues in Environmental Matrices

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Antibiotics concentrations were quantified for soil, runoff, and manure slurry samples. Target compounds, chosen based on the usage data from the facility operator and expected persistence or chemical properties of the parent compounds, were chlortetracycline, lincomycin, tiamulin, penicillin G and its degradation product penillic acid. Analytes were extracted and purified from liquid and solid samples and concentrated using polymeric (Oasis HLB 200 mg, Waters Corporation, Milford, MA) solid phase extraction. Oleandomycin was used as surrogate, while roxithromycin, doxycycline, and penicillin V were used as internal standards. Results of method validation indicated detection limits ranged between 0.005 and 0.014 μg/L in water, and between 0.14 and 0.68 ng/g in soil. Concentrated extracts were analyzed on a Waters Quattro Micro triple quadrupole mass spectrometer coupled with a Waters 2695 high pressure liquid chromatography (HPLC). Additional detail about the processing and analytical methods is reported in the Supplementary information file. Surrogate recovery averaged 107 ± 62% in runoff samples and 80 ± 35% in soil samples. Method detection limits for the analytes in various sample matrices are reported in Table S2.
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2

Synthesis of Monoterpene Derivatives

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Chemicals, such as acetone (purity ≥ 99.8%), dichloromethane (99.9%), ethyl acetate (99.9%), and n-hexane (99%), were purchased from Carl Roth (Arlesheim, Basel-Landschaft, Switzerland). (S)-2-methylbutanoic acid (98%), N,N’-dicyclohexylcarbodiimide (DCC, 99%), diethyl ether (stabilized, 99.8%), 4-N,N’-diméthylaminopyridine (DMAP, 99%), HCl (Titrisol, Buenos Aires, Argentina), magnesium sulfate (99.5%), methyl isonicotinate (98%), neryl acetate (97%), p-anisaldehyde (98%), petroleum benzine (b.p. 40–60 °C), (S)-(-)-verbenone (94%), sodium hydrogenocarbonate (99.7%), SilicaGel (230–400 mesh), and activated charcoal (for GC) were purchased from Sigma–Aldrich (Buchs, Saint-Gallen, Switzerland). Solid-phase extraction (SPE) cartridges OASIS HLB 200 mg were purchased from Waters (Baden-Dättwil, Aargau, Switzerland).
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3

Quinoa Aglycones Extraction and Analysis

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For the cell experiments, quinoa aglycones were extracted in order to assess the isolated effects on the intestinal transport. Half a gram of quinoa flour was weighed into a 50 mL centrifuge tube and suspended in 9 mL 50% methanol (Fluka, Steinheim, Germany) in MilliQ water (v/v) for 1 h at room temperature while shaking. The suspension was centrifuged at 4030 g for 5 min and subsequently mixed with 2 mL HCl (Emsure, Merch, Kenilworth, NJ, US) for hydrolysis at 80 °C for 90 min. Solid phase extraction (SPE) cartridges (Oasis HLB 200 mg, Waters, Etten-Leur, The Netherlands) were used for sample purification using a vacuum manifold. Columns were activated with 3 mL methanol followed by 3 mL MilliQ water. One mL of the quinoa extract was added to the columns followed by washing with 5 mL MilliQ water. The quinoa aglycones were eluted from the columns using 3 mL methanol. The eluates were dried under a steam of nitrogen at 50 °C for approximately 30 min.
Quantification of quinoa aglycones were assessed by HPLC-ESI-QTOF-MS.
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4

Quantitative Analysis of Water Contaminants

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Water samples were shipped frozen to Santiago de Compostela, where they were subjected to solid-phase extraction (SPE) within 48. Samples (200 mL) were filtered, spiked with 18 different isotopically labelled chemicals, used as internal standards (IS) and subject to SPE on Oasis HLB 200 mg (Waters, Milford, MA, USA) cartridges.
These were eluted with methanol, which was evaporated and made to a final volume of 0.5 mL. These samples were then analyzed on an LC-quadrupole-time-of-flight-HRMS Agilent system in both data-dependent and data-independent acquisition modes (DDA and DIA). Chemicals which were tentatively identified were integrated and normalized to an IS, in order to account for matrix effects. Procedural blanks were run with the samples and chemicals detected in the blanks were excluded.
Further details on sample preparation and analysis are provided in the Supporting Information (Text S1).
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