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Gc 2014 gas chromatograph

Manufactured by Shimadzu
Sourced in Japan, United States

The GC-2014 gas chromatograph is a laboratory instrument designed for the separation and analysis of complex chemical mixtures. It is capable of identifying and quantifying individual components within a sample. The GC-2014 utilizes a heated injection port, a separation column, and a detector to perform gas chromatography. This equipment is suitable for a wide range of applications, including environmental analysis, food and beverage testing, and chemical research.

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63 protocols using gc 2014 gas chromatograph

1

Biogas Production Measurement Protocol

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Samples were collected in the last three cycles of each batch. Biogas produced by the reactors was collected using water displacement for volume and rate measurement. After moisture removal, CH4 concentration was determined using a GC-2014 Gas Chromatograph (Shimadzu) equipped with a Molecular Sieve 13X packed column (2000 × 2 mm, Restek) and a thermal conductivity detector. For chemical measurements, effluent samples were filtered through 0.22 µm membranes. Soluble COD was measured with a COD digestion kit and DR/4000 U Spectrophotometer (HACH). TOC was measured with a TOC-V Analyzer (Shimadzu). VFAs were measured with a 1200 Series HPLC System equipped with a Hi-Plex H column for organic acids (Agilent). Ethanol concentration was measured with a GC-2014 Gas Chromatograph (Shimadzu) equipped with a flame ionization detector. The pH of the effluent was measured using a benchtop pH meter (Fisher). Current production resulted from poised potential was recorded with the manufacturer's software (BioLogic), and CE was calculated as previously described68 (link).
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2

Fatty Acid Profiling of Steer Serum

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Duplicate 1 mL serum aliquots from all steers were lyophilized (HarvestRight, North Salt Lake, UT, USA) and then transmethylated according to Park and Goins [17 (link)]. An internal standard, methyl tricosanoic (C23:0) was incorporated into each sample during methylation. Each sample of fatty acid methyl esters was analyzed using a Shimadzu GC-2014 gas chromatograph equipped with a Shimadzu AOC-20s automatic sampler. Separations were completed using a 60 m high resolution gas chromatography column (Agilent Technologies, Inc., Santa Clara, CA, USA). Samples were run at a split ratio of 10:1. Fatty acids were identified by comparing the retention times of known standards.
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3

Comprehensive Spectroscopic Characterization

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NMR spectra were recorded on a JEOL JNM-LA 400 spectrometer. UV-Vis spectra were recorded on a SHIMADZU UV-2550UV-Vis spectrophotometer or a UV-Vis Agilent Cary8454 spectrophotometer with a conventional quartz cuvette (path length, l = 1 cm). Spectroelectrochemical studies were performed using a BAS Inc. spectroelectrochemical quartz cell (l = 1 mm) containing Pt gauze (working electrode), a Pt wire (auxiliary electrode) and Ag/Ag+ (reference electrode) in conjunction with a CH Instruments potentiostat. Elemental analyses were performed on a J-SCIENCE LAB MICRO CORDER JM10 elemental analyser. ESI-TOF mass spectra were recorded on a JEOL JMS-T100LP mass spectrometer. Gas chromatography analysis of O2 was performed using a Shimadzu GC-2014 gas chromatograph equipped with a thermal conductivity detector and fitted with a molecular sieve (5 Å) column, and the system was calibrated with air. Dynamic light scattering (DLS) data were measured using a Photal OTSUKA ELECTRONICS ELSZ-1000 zeta-potential and particle size analyser, equipped with a 785 nm red laser source (detection limit: 0.6 nm particle diameter).
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4

Comprehensive Wastewater Characterization Methods

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Total solids (TS), total suspended solids (TSS), volatile suspended solids (VSS), volatile solids (VS), Kjeldahl nitrogen (TKN) and total COD were measured according to Standard Methods (Greenberg et al. 1992) . Soluble COD was measured using Nanocolor COD1500 or 15000 test kits (Machery-Nagel, Düren, Germany), according to the manufacturer's instructions. The concentrations of NH4 + , Na + and K + were measured on a 761 Compact Ion Chromatograph (Metrohm, Herisau, Switzerland), which was equipped with a Metrosep C6-250/4.0 main column, a Metrosep C4 Guard/4.0 guard column and a conductivity detector. The eluent contained 1.7 mM HNO3 and 1.7 mM dipicolinic acid. Samples were centrifuged at 3000g for 3 min with a Labofuge 400 Heraeus centrifuge (Thermo Fisher Scientific Inc, Merelbeke, Belgium), filtered over a 0.22 µm filter (type PA-45/25, Macherey-Nagel, Germany) and diluted with Milli-Q water to reach the desired concentration range for quantification between 1 and 100 mg L -1 . The pH was measured with a C532 pH meter, and conductivity was determined with a C833 conductivity meter (Consort, Turnhout, Belgium). The biogas composition was measured using a Compact Gas Chromatograph (Global Analyser Solutions, Breda, The Netherlands) (S5). The different VFA (C2-C8) were measured with a GC-2014 Gas Chromatograph (Shimadzu®, The Netherlands) (S6).
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5

Mango Respiration Rates in Cold Storage

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Red and green mango fruit cv. Shelly were stored at 5, 8 or 12 °C. Eight red-colored and eight green-colored fruit were enclosed in glass jars (one fruit per jar). The respiration production rates of the mango fruit were measured by closing the bottles for 1 h. Samples were taken using syringes and subsequently analyzed by GC for CO2 (GC-2014 gas chromatograph, Shimadzu, Tokyo, Japan) and for ethylene (Varian Model 3300 GC, Agilent Technologies, Santa Clara, CA, USA). The respiration rate was measured after harvest, and after 1 week and 3 weeks in cold storage.
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6

Analysis of Short-Chain and Branched-Chain Fatty Acids in Intestinal Samples

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The dialysate and lumen fractions of TIM-2 were analyzed with gas chromatography for SCFA (acetate, propionate and butyrate) and BCFA (iso-butyric acid and iso-valeric acid).
For SCFA/BCFA, samples were prepared and analyzed as described previously [10 (link)]. Briefly, dialysate samples were directly used, lumen samples were centrifuged (12,000 rpm at 4 °C for 10 min). A mixture of formic acid (20%), methanol, and 2-ethyl butyric acid (internal standard, 2 mg/mL in methanol) was added to the supernatant. A 3 μL sample with a split ratio of 75.0 was injected on a GC-column (ZB-5HT inferno, ID 0.52 mm, film thickness 0.10 um; Zebron; Phenomenex, Utrecht, The Netherlands) in a Shimadzu GC-2014 gas chromatograph (Shimadzu Europe, Duisburg, Germany).
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7

Groundwater Characterization at Outflow

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The physical and chemical parameters of the groundwater were measured at the groundwater outflow of the deep well. Temperature was measured with a CT-460WR thermometer (Custom, Tokyo, Japan). Oxidation-reduction potential (ORP) and pH were measured with RM-20P and HM-20P portable meters (DKK-TOA, Tokyo, Japan), respectively. Electric conductivity (EC) was measured with a CM-21P portable meter (DKK-TOA). Concentrations of natural gas were determined on a GC-2014 gas chromatograph (GC) equipped with a thermal conductivity detector (TCD) and a flame ionization detector (Shimadzu, Kyoto, Japan) following the procedures described by Matsushita et al. [10 (link)].
The concentrations of anions (Cl, Br, I, F, PO43−, NO3, SO42−, HCO3, acetate, and formate) and cations (Na+, Ca2+, Mg2+, K+, and NH4+) in the groundwater were analyzed with an ICS-1500 ion chromatography system (Dionex, Sunnyvale, CA, USA). Sulfide was analyzed by a sulfide ion detector (Gastech, Ayase-Shi, Kanagawa, Japan). Dissolved organic carbon (DOC) in the groundwater filtered through pre-combusted GF/F glass microfiber filters (GE Healthcare, Buckinghamshire, UK) was measured with a TOC-V total organic carbon analyzer (Shimadzu).
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8

Photocatalytic H2 Production from Formic Acid

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The setup for
H2 evolution from formic acid dehydrogenation is shown
in Figure S2. In a typical experiment,
a vial (70 mL) containing a Au–Cu/TiO2 film (19
mm × 19 mm) immersed in formic acid (0.010 M, 30 mL) was sealed
using a rubber septum and Teflon tape. The reactor was deaerated before
the reaction by purging Ar for 30 min. The formic acid solution was
stirred continuously to ensure homogeneous distribution and reaction
with the photocatalyst film. Thereafter, the vial was irradiated using
an LED lamp (λ = 365 nm) to initiate H2 evolution
from formic acid dehydrogenation. The intensity of the light irradiated
on the photocatalyst films was adjusted to be 4.3–30 mW cm–2. After every 60 min of the irradiation, the gas evolved
in the headspace (40 mL) of the reaction vial was sampled using a
gastight syringe (100 μL) and quantified using a Shimadzu GC-2014
gas chromatograph (Ar carrier gas, Shincarbon-ST column) equipped
with a thermal conductivity detector.
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9

Fatty Acid Profiling of Poultry Fats

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Samples of fat (200 g; 65% abdominal fat and 35% gizzard fat, the normal fat proportions of the carcass) were dried and extracted following the Soxhlet procedure and using diethyl ether as the extraction solvent [11 ]. The methyl esters from fatty acids (FAME) were prepared using BF3 in methanol and stored at −80 °C until chromatographic analysis.
The FAME were analysed using a gas chromatograph (GC-2014 Gas Chromatograph, Shimadzu, Chiyoda-ku, Tokyo, Japan) equipped with a flame ionization detector, a split/splitless injector, and a fused silica capillary column containing polyethylene glycol as stationary phase (db-wax, 60 m × 0.25 mm, J&W Scientific, Santa Clara, CA, USA). The injector temperature was set to 230 °C. The initial column temperature was 80 °C for 2 min at a rate of 3 °C per minute, was raised to 180 °C at 30 °C per minute and was kept at this temperature for 30 min. After this time, the temperature was increased to 200 °C at a rate of 3 °C per minute and remained at this temperature for 108 min. The fatty acids were quantified using C11:0 methyl ester as internal standard. Identification of fatty acids was performed by comparison of the retention times with those of known fatty acids and the results expressed as percentage of the area of each fatty acid over the total area of fatty acids (%).
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10

Measuring Short-Chain Fatty Acids

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We collected 2 mL of fresh culture, which we then centrifuged at 10,000× g for 15 min. The supernatants were filtered (filter with 0.2 µm pores) and stored at −20°C until analysis. Samples for short-chain fatty acid (SCFA) analyses were collected after 16, 22, and 40 h. SCFAs were extracted from the samples in diethyl ether, after the addition of 2-methyl hexanoic acid as an internal standard. Extracts were analyzed with a GC-2014 gas chromatograph (Shimadzu, ’s-Hertogenbosch, The Netherlands), equipped with a capillary fatty acid-free EC-1000 Econo-Cap column (dimensions: 25 mm × 0.53 mm, film thickness: 1.2 mM; Alltech, Laarne, Belgium), a flame ionization detector and a split injector.
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