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Gs gaspro capillary column

Manufactured by Agilent Technologies
Sourced in United States

The GS-GasPro capillary column is a high-performance gas chromatography (GC) column designed for a wide range of applications. It features a unique stationary phase that provides efficient separation and inert characteristics, making it suitable for analyzing a variety of volatile and semi-volatile compounds.

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5 protocols using gs gaspro capillary column

1

Gaseous Products Analysis by Gas Chromatography

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The analysis of the gaseous products was carried out by means of a gas chromatograph Chromatek-5000 using a gas extracting cell. The cell is an improved version of a previously described modification19 (link). The present gas extracting cell (Supplementary Figure 4 in the Supplemental Materials) allows us to send the gas mixture directly from the capsule into the gas chromatograph. After the capsule was taken from the pressure equipment it was placed inside the cell and sealed inside with a rubber ring. After air was taken from the cell by the first blow, a hard alloy needle penetrated the capsule. After penetration, the gas spread out inside the cell and was then sent to the chromatograph for analysis by the second blow.
The specification of the chromatograph Chromatek-5000 was focused on the detection and separation of light hydrocarbons by an Agilent GS-GasPro capillary column in an increasing temperature regime from 60 to 140 °C in 50 min. The column allows to detect even neglectable quantity of the hydrocarbon gas produced. The detection of the separated hydrocarbon components was carried out by the FID detector.
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2

Monitoring Dhb sp. UNSWDHB Cell Growth

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To monitor optimal growth of Dhb sp. UNSWDHB cells, the chlorinated methanes in the cultures (reduction of CF to DCM) were monitored by headspace analysis using an Agilent Technologies gas chromatograph equipped with a flame ionization detector (GC‐FID) and a GS‐GasPro capillary column (60 × 0.32 mm), as described elsewhere (Lee et al., 2012). Inlet and detector temperatures were set at 250°C, the oven temperature was programmed as follows: 1 min at 100°C followed by a gradient of 25°C min−1 increasing to 250°C where held for 5 min. The retention times of DCM and CF were 5.3 and 6 min, respectively, at a flowrate of 3 ml min−1.
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3

Quantifying Methyl Chloride Levels via GC-MS

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CH3Cl was measured in headspace gas volume by injecting 100 μL of a headspace gas sample into a ISQTM Quadrupole GC–MS System using a TRACETM Ultra gas chromatograph (Thermo Fisher Scientific, USA) fitted with a 60 m, 0.32 mm GS-GasPro capillary column (Agilent Technologies, California, USA) with helium as the carrier gas (constant column flow rate, 1.5 mL min−1). Headspace gas samples (100 μL) were injected into the column with a temperature ramp from 40 to 200 °C (15 °C increase min−1). High-throughput measurements were carried out by the MultiPurpose autosampler MPS (Gerstel Inc., USA). Chromatograms were analyzed with the software Openchrome® (Lablicate GmbH, Germany). CH3Cl concentrations were calculated by regression analysis based on a six-point calibration with CH3Cl standard ranging from 10 to 150 mM.
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4

Gas-Phase Pollutant Removal Kinetics in Biofilters

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Gas-phase concentrations were measured with a gas chromatograph (Shimadzu GC-2010, Japan) equipped with an FPD detector. The column used was a GS-Gas Pro capillary column (30 m × 0.32 mm × 1.0 μm, Agilent Technologies, USA). Gas samples were taken using Tedlar bags of 2 L. Total volume of 100 μL was injected into the GC using a gastight syringe. The injector and detector temperature were set at 70 °C and 250 °C, respectively. The GC oven temperature was programmed as follows: initial temperature of 80 °C for 2 min, increase to 250 °C at 10 °C min− 1 and maintain for 5 min.
Macro-kinetic model was used to evaluate the elimination capacities (ECs) of each BTF. The ECs commonly follow a behavior that can be adequately described by a Michaelis-Menten model type [36 (link)]. This model is constructed based on ECs and is relatively simple and useful in predicting the removal performance of practical engineering.
EC=ECmaxClnKs+Cln
Where ECmax (g.m3/h) is the maximum elimination capacity, Cln (g/m3) is the logarithmic average of the inlet and outlet concentrations of pollutants in the gas phase and Ks (g/m3) is the saturation constant.
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5

Quantitative Analysis of Biofilm Reactor

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The pH of the nutrient solution was measured on-line using a pH-meter. To determine the pH of the different layers of the BTFs bed, before each transient experiment, triplicate samples of the packing were taken from the each sampling site using a sterile tweezers, mixed with 3 mL of sterile water, and centrifuged at 7000 rpm for 10 min; the supernatants were analyzed with the pH-meter, and the pellets were used to measure the biomass. The biomass concentration was quantified based on the total protein measurement using the Bradford method. Sulfate, thiosulfate, nitrate and nitrite were analyzed using an ion chromatograph (Dionex ICS-1500, USA) with an AS19/AG19 column (Dionex, USA).
To analyze the H2S concentration, gas samples were collected in 2 L Tedlar bags, and immediately analyzed with a gas chromatograph (Shimadzu GC-2010, Japan) equipped with an FPD detector. The air was separated by a GS-GasPro capillary column (30 m × 0.32 mm × 1.0 μm, Agilent Technologies, USA) with nitrogen as the carrier gas at a flow rate of 1.5 mL/min. The injector and detector temperature were 70°C and 250°C, respectively. The GC oven temperature was programmed as follows: initial temperature of 80°C for 2 min, increase to 250°C at 10°C min−1 and maintain for 5 min.
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