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Ionpac as18

Manufactured by Thermo Fisher Scientific
Sourced in United States

The IonPac AS18 is an ion exchange chromatography column designed for the separation and analysis of anions. It features a high-capacity, latex-based, polymer-based stationary phase that provides efficient and selective separation of a wide range of inorganic and organic anions.

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9 protocols using ionpac as18

1

Ion Chromatography Analysis of Plasma Activated DI Water

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Plasma activated DI water was analysed using an ion chromatography system (Integrion RFIC, Thermo Fisher Scientific, Waltham, MA) coupled with a conductivity detector. A Dionex IonPac™ AS18 anion exchange column (4 × 250 mm) maintained at 30 °C was employed as the stationary phase. A flow rate of 1 mL min−1 and injection volume of 250 μL was used to carry out the anion test for fluoride, chloride, nitrite, bromide, sulphate, nitrate, and phosphate ions, respectively.
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2

Arsenic Speciation Analysis Utilizing Ion Chromatography

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Arsenic speciation was investigated with the use of ion chromatography on an IonPac AS18 (2 mm, Dionex, Lübeck, Germany) column on an ICS Dionex 3000 (Lübeck, Germany) instrument equipped with an ASRS® 2 mm suppressor, which was coupled to a ZQ 2000 mass spectrometer via an electrospray source (Waters, Milford, MA, USA) according to the method described by Debiec et al. [9 (link)]. In the adsorption module, the total arsenic concentration was investigated. Total arsenic concentration was measured using a Graphite Furnace Atomic Absorption Spectrometry (GFAAS; AA Solaar M6 Spectrometer, TJA Solutions, Waltham, MA, USA). Arsenic standard solutions (Merck, Darmstadt, Germany) were prepared in 3% HNO3. The pH and redox potential were measured only in the microbiological module. Samples of raw water, water from the bioreactor, as well as water at the inflow and outflow of each adsorption column were collected once a day during the first 8 days, and then three times a week up to day 40. Samples taken from the bioreactor were stored at −20 °C, while samples collected from the adsorption module were stored at 4 °C. This experiment was repeated twice.
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3

Butylparaben Photodegradation Kinetics

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The butylparaben decay rate was monitored by high pressure liquid chromatography (HPLC) coupled with UV detection using a Waters apparatus. Analysis was performed with a Waters Nova-Pak C18 column (3.9 mm × 150 mm) using a mobile phase consisting of a degassed mixture (70/30, v/v %) of methanol and acidified water (0.01% orthophosphoric acid) at a constant flow of 1 mL min−1. The detailed description of this analysis of BP is reported elsewhere [19 (link),23 (link)]. The spectrophotometric analysis was performed on a Unicam UV 300 spectrophotometer. The dissolved organic carbon measurements were performed on a HACH IL 550TOC-TN apparatus. The ion concentrations were determined by an ion chromatograph (Dionex model ICS) on an IonPac CS18 (for cations) and an IonPac AS18 (for anions).
The performed experiments allowed us to estimate the extent of direct reaction of butylparaben with hydrogen peroxide in the absence of radiation, (“dark reaction”).
Results indicated an insignificant role of the direct reaction of studied compounds with H2O2. The blank reaction was carried out to investigate the hydrolysis of BP. The experiments showed no decomposition of the investigated compound in the dark after 12 h, much longer time than used during the photodegradation.
Experiments were performed in duplicate to assure accurate data acquisition.
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4

Quantification of Nitrite and Nitrate Ions

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Before the measurements, the sample solution (pH of the sample solution was 5.4) was diluted tenfold with deionized water with a resistivity of 18 MΩ cm, obtained from a Milli‐Q water purification system (Millipore, Bedford, MA, USA). For NO2 and NO3 determination, an ionic chromatography system Dionex, ICS 3000 was used under the following experimental conditions: eluent: 23 mm KOH, eluent source: EGC‐KOH II cartridge, flow rate: 1 mL min−1, temperature: 30 °C, detection: suppressed conductivity, suppressor: Dionex ERS 500, 4 mm; auto‐suppression recycle mode, columns: Dionex IonPac AG 18 (4×50 mm) (precolumn) and Dionex IonPac AS 18 (4×250 mm), injection volume: 50 μL, pump flow rate precision: <0.1 %, pump flow rate accuracy: <0.1 %.
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5

Geochemical Porewater Analysis

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Sulfate and chloride concentrations were measured by suppressed ion chromatography with an ICS2500 system (Dionex) equipped with an eluent generator (EG50) and KOH eluent generator cartridge (EGC III KOH). The column was a Dionex IonPac™ AS18 operated at 30°C. KOH concentration started at 20 mmol L−1 and was raised to 32 mmol L−1 at the end of the analysis run at 15 min. Hydrogen sulfide (sum of H2S, HS and S2−) was determined spectrophotometrically at 670 nm (FLUOstar Omega, BMG Labtech GmbH, Orthenberg, Germany) on zinc-preserved porewater samples by the methylene blue method (Cline, 1969 ; Reese et al., 2011 (link)). DIC was measured immediately after the cruise on headspace-free porewater samples stored at 4°C. Samples were transferred to sealed exetainers and acidified with 85% (v:v) phosphoric acid. After 24 h of equilibration time, the produced CO2 was measured from the headspace of the exetainer by a Delta V™ isotope ratio mass spectrometer (IRMS, Thermo Scientific).
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6

Phosphate Determination via Ion Chromatography

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The determination of phosphate, as phosphorous (PO4-P), was performed utilizing ICS-2000 (Dionex) ion chromatographic system, with ultimate 3000 autosampler. An ion exchange column specifically designed for rapid analysis of inorganic anion (Dionex IonPac AS18, 4 x 250 mm) equipped with an IonPac guard column (Dionex IonPac AG18, 4 x 50 mm) was used.
Chromeleon® software was used to acquire data and control the instrumentation. Calibration standards and samples were filtered using 0.45 µm Nylon membrane filter before injection.
Error in the measurements is < 1.2%.
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7

Ion Chromatography Analysis of Atmospheric Samples

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The concentrations
of major ions were measured using two Dionex Integrion high-pressure
ion chromatography (HPIC, Thermo Fischer Scientific, USA) instruments.
Samples and blanks were prepared by filling ion chromatography vials
with 5 mL of the ∼10 mL final eluates from the solid-phase
extractions. The autosampler split the volume of each sample between
the two HPIC instruments, with one column to quantify the cations
(IonPac CS12A, Thermo Fischer Scientific, USA) and the other to quantify
the anions (IonPac AS18, Thermo Fischer Scientific, USA). Here, we
measured the concentrations of cations lithium, sodium, ammonium,
potassium, magnesium, and calcium and anions fluoride, acetate, formate,
chloride, nitrite, carbonate, sulfate, and nitrate in each solution.
The concentrations of the corresponding sample blanks were subtracted
from the samples. Concentrations in solution were calculated from
calibration curves for each ion of interest. Ion concentrations in
particle samples were derived using the total volume of air sampled.
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8

Comprehensive Analysis of Culture Samples

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The pH of the culture samples obtained during the incubation was measured using a pH meter (Seven Compact S220, Mettler Toledo, United States). The cultures were then centrifuged for 10 min at 3,900 g (Allegra X-22R, Beckman Coulter, United States). The supernatant obtained after centrifugation was analysed for total alkalinity (TA), anions, cations, and total nitrogen concentrations. In brief, TA was measured using a G20 compact titrator (Mettler Toledo, United States); 40 ml of supernatant was taken in a beaker and titrated with 0.2N H2SO4 until the samples reached an endpoint of pH = 4.3 (Vadlamani et al., 2019 (link)). Bicarbonate and carbonate concentrations were calculated using the measured pH and total alkalinity (TA) (Vadlamani et al., 2017 (link); Vadlamani et al., 2019 (link)).
The nitrate concentration was measured using an ion chromatograph equipped with an IonPac AS18 anion and a conductivity detector (DIONEX ICS 2000; Thermo Fisher, United States) (Vadlamani et al., 2017 (link); Vadlamani et al., 2019 (link)). The ammonium concentration was determined colorimetrically as previously described (Sims et al., 1995 (link)). The total nitrogen concentration was assessed using a scaled down version of the Persulfate Digestion method (Hach Method 10071, Hach, United States) (Vadlamani et al., 2017 (link); Vadlamani et al., 2019 (link)).
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9

Analyzing Hot Spring Water Composition

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Major cation and anion concentration of the hot spring water was measured using ion chromatograph (IonPac AS18 4 × 250 mm for anion, ICS 600, ThermoFisher, Carlsbad, CA, USA). The DOC and TOC contents were measured by using an NC 2100 Elemental Analyzer (multi N/C 2100, Analytic Jena, Jena, Überlingen, Germany). Before TOC measurements, the sampled sediments were fumigated with HCl to remove carbonates.
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