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Ics 5000 dc

Manufactured by Thermo Fisher Scientific
Sourced in United States

The ICS-5000+ DC is an ion chromatography system designed for the analysis of inorganic anions and cations. It provides precise and reliable ion separation and detection capabilities for a variety of sample types.

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6 protocols using ics 5000 dc

1

Hemicellulose and Acid-Insoluble Solids Analysis

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The hemicellulose content and amount of acid-insoluble solids were measured according to previous studies [23 (link)]. Ten milliliters of the liquid samples was mixed with 750 µL 72% sulfuric acid and autoclaved (Systec DX 150, Wettenberg, Germany) at 121 °C for 1 h to hydrolyze the polymeric sugars. The samples were then filtered to remove insoluble solids, and the filters were dried overnight in an oven at 105 °C. The acid-insoluble solids content was determined by measuring the dried filters before and after filtration of the samples.
The hemicellulose content was determined by analyzing the liquid fraction after the filtration by high-performance anion-exchange chromatography (HPAEC). The HPAEC system (ICS-5000+ DC, Dionex, Sunnyvale, CA, USA) was a pulsed amperometric detector with a compartment temperature of 30 °C, and the separation was performed on a Carbo Pac PA1 analytical column. Deionized water at 1 mL/min was used as the main eluent, and 200 mM sodium hydroxide solution was used as the postcolumn addition at 0.5 mL/min. The samples were diluted with deionized water, and the injection volume for the HPAEC was 10 µL for all samples. The standards were D-mannose, D-xylose, D-glucose, D-galactose, and L-arabinose (Fluka Chemie AG, Buchs, Switzerland), and the hemicellulose content was determined after anhydro corrections of 0.90 for hexoses and 0.88 for pentoses.
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2

Quantitative Metabolite Profiling by GC-TOF-MS

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Polar metabolites were extracted, derivatized and run on the GC-TOF-MS as described before (Ribeiro et al. 2014 (link)) but 5 mg of dry material was used instead of 20 mg. All volumes were stoichiometrically adjusted.
In order to confirm the sucrose trend from GC-TOF-MS, soluble carbohydrates were also determined as described previously (Ribeiro et al. 2014 (link)). The supernatant after starch extraction was injected into a Dionex HPLC system (ICS 5000 + DC) to analyse the soluble carbohydrate content, using a CarboPac PA 1, 4- × 250-mm column preceded by a guard column (CarboPac PA 1, 4 × 50 mm), and a gradient pump module (ICS 5000 Dual Pump, Dionex). Mono-, di-, and tri-saccharides were separated by elution in an increasing concentration of NaOH (20–350 mM) with a flow rate of 1 mL min−1. Peaks were identified by co-elution of soluble carbohydrate standards. Sugar quantity was corrected by mean of the internal standard (melezitose) and transformed to micrograms of sugar per milligram of dry material.
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3

Determination of Hemicellulose Content

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The hemicellulose content was determined according to a standardized National Renewable Energy Laboratory (NREL) method [19 ]. The samples were acid hydrolyzed by adding 750 µl 72% sulfuric acid to 10 mL sample and autoclaved (Systec DX 150, Wettenberg, Germany) at 121 °C for 1 h. The samples were thereafter filtered to remove the acid-insoluble solids. The filter was then dried and weighed to determine the acid insoluble content. The filtrate was diluted with deionized water and analyzed with high-performance anion-exchange chromatography (HPAEC). The HPAEC system consisted of an ICS-5000+ DC (Dionex, Sunnyvale, CA, USA) equipped with pulsed amperometric detection running at a compartment temperature of 30 °C. The different monosaccharides were separated using a Carbo Pac PA1 analytical column where the eluent was deionized water at a flow of 1 and 0.5 mL/min 200 mM sodium hydroxide solution post-column addition. The injection volume was 10 µl and the standards used were L-arabinose, D-galactose, D-glucose, D-xylose, and D-mannose all manufactured by Fluka Chemie AG (Buchs, Switzerland). The amount of hemicellulose was determined after anhydro corrections of 0.90 for hexoses and 0.88 for pentoses.
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4

Quantitative Analysis of Water-Soluble Anions

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A test tube with a stopper that holds 50 mL of ultrapure water and 15 mL of each exposed filter paper was placed in an ultrasonic bath. The soluble components were separated by centrifuging at 2500 rpm for 10 min. The supernatant solution was filtered twice using membrane filters made of nylon and hydrophilized poly(tetrafluoroethylene) with pore diameters of 0.45 m and 0.2 m, respectively, and then refrigerated until analysis for water-soluble anions like Cl, NO3, and SO42− were studied using an ion chromatograph (Mahapatra et al., 2013 (link)), “Model no. DIONEX ICS-5000+ DC”.
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5

Comprehensive Analysis of Pit Mud Composition

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Pit mud moisture levels were established by drying samples for 3 h at 115 °C. Pit mud pH values were established with a Mettler Toledo pH meter after diluting sample 1:4 (w/v) with dH2O for 3 h. Pit mud ammonium (NH4+-N) levels were established via extraction in 10% (w/v) NaCl at a 1:10 (w/v) ratio, after which concentrations were measured using a UV spectrophotometer. Acetic acid, butyric acid, and caproic acid were extracted using 15% methanol and quantified via gas chromatography (Agilent 7890, Santa Clara, CA, USA) as described previously [12 (link)]. Lactic acid (LA) levels were quantified via ultra-high-performance liquid chromatography (UPLC, Acquity I-class, Waters, Milford, MA, USA) as previously reported [1 ]. Levels of K+, PO43−, soluble Mg2+, and soluble Ca2+ in air-dried pit mud were measured via extracting samples with ddH2O at a 1:10 (w/v) ratio, after which concentrations were measured as reported previously by Zhang et al. using an ion chromatograph (ICS5000+, Thermo Fisher, Waltham, MA, USA) equipped with a conductivity detector (ICS-5000+-DC) and a CS12 column (Ion Pac, Thermo Fisher, 4 mm × 250 mm) [4 (link)]. The utilized injection volume was 25 μL, with methane sulfonic acid (20 mM) as a carrier fluid at a 1 mL/min flow rate, with a column temperature of 30 °C. Humus levels were determined as detailed previously by Shen [13 ].
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6

Arsenic Speciation in Soil Porewaters

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Arsenic species in 0.4 micron Millipore membrane filtered soil porewaters (iAs, MMA, DMA, TMAO and TETRA) were determined using a Dionex IC chromatographic system interfaced with ICP-MS (ICS-5000 DC, Thermo Scientific) as outlined in detail in Signes-Pastor et al. 5, 26 Using an arsenic speciation specific IC-column, IC-ICP-MS, unlike HPLCanion exchange -ICP-MS, separates TMAO, and we run authentic TMAO samples, and cross validate with cation exchange IC-ICP-MS 27 . We have added TMAO to the list of analytes detected in soil porewaters. Results were expressed on a per kg soil (g/kg) and statistical analysis performed in Minitab as outlined below.
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