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Gc 450

Manufactured by Agilent Technologies

The GC-450 is a gas chromatography (GC) system designed for analytical applications. It provides reliable and efficient separation and detection of a wide range of chemical compounds. The GC-450 features advanced technology to ensure accurate and reproducible results.

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12 protocols using gc 450

1

Urinary Metabolite Quantification by GC-MS/MS

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Single, spot urine samples were collected and frozen at – 20 °C and sent to the laboratory in the Department of Toxicology, Medical University of Gdańsk. Analyses were performed using gas chromatography (Varian GC-450) coupled with tandem mass spectrometry (Varian 220-MS, ion-trap mass spectrometer).
Three milliliters of urine was placed in 10-ml screw-cap glass tube followed by 50 μl of mixed internal standard solution and 750 μl of freshly prepared acetate buffer (1 M, pH 5.0) containing 230 U of β-glucuronidase was added. Overnight incubation (at least 12 h) at 37 °C was performed. Then the sample was acidified with 450 μl of 80% formic acid and 3 ml of HEX:MTBE mixture (3:1, v:v) was added to the sample and tube was shaken for 10 min. After centrifugation, the organic layer was transferred into open glass tube and the extraction was repeated. Combined extracts were cleaned-up with 200 mg of MgSO4 and 10 mg of PSA by shaking in hands for 1 min. Then 5 ml of cleaned extract was transferred into new open glass tube and evaporated to dryness under stream of nitrogen at 35 °C. The residue was dissolved with 50 μl of BSTFA:TMCS (99:1) and derivatized for 30 min at 40 °C. One microliter of final extract was analyzed by GC-MS/MS. The limit of detection was 0.5 μg/L.
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2

GC-MS Analysis of Chemical Compounds

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Analyses were performed using GC (Varian GC-450) coupled with tandem MS (Varian 220-MS, ion-trap mass spectrometer). Separation was achieved on a VF-5ms (Varian, Palo Alto, USA) low bleed capillary column (30 m × 0.25 mm inner diameter, 0.25-μm film thickness with integrated 10-m guard column) using the following temperature oven program: 60°C for 3 min, 60–140°C (120°C/min), 140–290°C (17°C/min), 280°C held for 13 min. The flow rate of the carrier gas, helium, was 1.0 ml/min. Temperature of the manifold, trap, and transfer line were 45°C, 200°C, and 290°C, respectively.
One microliter of the sample extract was injected in splitless mode into a 1,177 split/splitless injector (injector temperature 280°C).
The limit of detection (LOD) was 0.5 µg/L.
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3

Comprehensive Biogas Substrate Analysis

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The pH value, dry matter content, acidity, alkalinity, content of fatty acids (acetic, propionic, butyric, and valeric), and COD were determined.
The content of fatty acids was determined by gas chromatography (Varian GC 450) with an FID detector (H2: 30 mL/min, air: 300 mL/min, He: 30 mL/min). Helium (constant flow through the 1mL/min column) was used as the carrier gas, 1:30 split.
The acidity and alkalinity were determined by pH-metric titration, according to standard methods [44 ]. The acidity/alkalinity ratio (index R) was also determined.
The suspended solids (SS) and dry organic mass were determined according to standard methods [44 ].
The chemical oxygen demand (COD) was established spectrophotometrically using Lange cuvette tests.
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4

Quantifying Bacterial Oxygen Consumption

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For determination of the oxygen consumption we designed two assays. First we evaluated the depletion of the oxygen levels in the gas phase of culture flasks sealed with Suba-seal septa. Every hour we took a 0.5 ml gas sample from the growing culture and analyzed the oxygen concentration by gas chromatography (Varian GC-450) coupled to a molecular sieve column and a TCD detector. Oxygen depletion was linear until 10 hours growth. The rate of consumption was calculated as the amount of oxygen consumed in the gas phase normalized by the protein concentration of the culture. A measurement of the dissolved oxygen consumption was also carried out with a Clark-type electrode. After addition of 100 μl of bacterial culture into the chamber, containing 1.6 ml of NFbHP-Malate at 30°C, the consumption of dissolved oxygen in the medium was recorded until the polarizing voltage reached 0 (i.e. 0% oxygen saturation).
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5

Methanol Dehydrogenation Reaction Catalysis

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The methanol dehydrogenation reaction
was carried out with a fixed-bed reactor. Prior to the reaction, 100
mg of catalyst was placed in the reactor and reduced by dilute hydrogen
(H2/N2 = 30 mL/min:20 mL/min) at 250 °C
for 3 h. After pretreatment, a stream of pure methanol solution was
first fed (0.1 mL/min) into an evaporator at 200 °C, and then
the methanol vapor was carried into the reactor by N2 (50
mL/min). Reaction products were analyzed using an online GC system
(Varian GC-450) connected with two channels, A and B. Channel A is
consisted of a set of three packed columns, “HayeSep”
Q (CP81073),“HayeSep” T (CP81072), and “MolSieve”
13X (CP81073), connected with a TCD detector to monitor CO and CO2. Channel B uses a CP-wax 52CB column (CP7668) and was connected
with a flame ionization detector to monitor MF and other oxygenates.
After a reaction time of 50 h, the spent catalyst was regenerated
by calcination for 3 h at 400 °C, under an air atmosphere, to
remove the coking. Once regenerated, the catalyst was reduced by dilute
H2 before undergoing the next round of the catalytic test
as previously described.
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6

Methane Detection via Gas Chromatography

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The gas phase was analyzed qualitatively for the presence of methane using a gas chromatography system (GC-450, Varian, Middelburg, The Netherlands) equipped with a molecular sieve column (CP81071: 1.5 m*1/8″ ultimetal molsieve 13 9 80–100 mesh) and a flame ionization detector.
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7

Triclosan Quantification in Urine Samples

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Urine samples were collected in a polypropylene cup. During each IVF-ICSI cycle, at least one urine sample was provided just before egg-retrieved procedure. A handheld refractometer was used to assessed specific gravity (SG). The concentration of triclosan was measured using gas chromatography (Varian GC-450) coupled with tandem mass spectrometry (Varian 220-MS, ion-trap mass spectrometer as previously described (Jurewicz et al. 2019 (link))). External quality control was carried out by participation in the German External Quality Control Scheme (G-EQUAS), organized, and managed by the Institute and the Outpatient Clinic for Occupational, Social, and Environmental Medicine of the University of Erlangen-Nuremberg (Erlangen, Germany). Scheme, evaluation, and certification are based on the German Federal Medical Council (http://www.g-equas.de/). Analytical laboratory of the Department of Toxicology, Medical University of Gdańsk, successfully participated in this external quality check for triclosan.
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8

Photocatalytic CO2 Reduction and Methanol Oxidation

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Before the photocatalytic reduction of CO2, 10 mg photocatalyst and 10 mL water were added into a septum-sealed borosilicate glass reactor with a volume of 140 mL. Then, the reactor was purged with CO2 for the photoreduction experiment. A 300 W Xe lamp (Newport) was utilised as a light source, and the light output power was measured by a Newport 918-D calibrated photodetector. During the reaction, the products were analysed by GC (Varian GC-450) with a thermal conductivity detector (TCD, connected to a molecular sieve column) and a flame ionisation detector (FID, connected to a CP-SIL 5CB capillary column) containing a methanizer equipment. Ar gas was used as the GC carrier gas.
For the isotope-trace experiment, the same photocatalytic process was applied except 13CO2 (13C 99%, Sigma-Aldrich) was used as the feed gas. The products containing C-isotope were analysed by GC–MS (Shimadzu QP-2010SE) with a molecular sieve 5 Å capillary column (for CO) or a Rxi-624Sil MS capillary column (for methanol). He gas was used as a carrier gas during the measurement.
The CH3OH oxidation conditions: 10 ml H2O, 0.12 µmol MeOH, 10 mg mCD/CN photocatalyst, 300 W Xenon lamp irradiation with 420 nm long-pass filter in 1 bar Argon atmosphere.
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9

Analytical Methods for Lignocellulosic Biomass

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The gas phase was analysed by using a Varian GC 450 equipped with a Shin-Carbon-column (2 m×0.75 mm), a TCD and a FID. The yield of CO 2 and CO were determined according to and .
The liquid phase was analysed using a Jasco HPLC (uncertainty of 0.86 %) equipped with a Shodex column SH1011 (300 mm×8 mm) and a Jasco JEATSTREAM1-PLUS oven. Prior to injection, the sample was filtered with a one-time Micropur PET filter (Altmann Analytik) with a pore width of 0.2 μm. The yield of formic acid was determined according to . The formic acid selectivity was determined using .
The conversion of the lignocellulosic substrates was determined by and represents the amount of all dissolved components into the IL.
The mass balances were calculated based on the initial carbon content in the lignocellulosic feedstocks considering all identified liquid and gaseous reaction products as well as the cellulose rich pulp.
After the reaction, the solid pulp was filtered, washed with H 2 O and methanol and dried in an oven at 40 °C overnight.
The acidity measurements of the reaction solutions were conducted using a pH-electrode of the type EC-25 of Phoenix instruments.
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10

Fatty Acid Methyl Ester (FAME) Analysis

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The methodological procedure described in a previous publication was used [6 (link)]. Approximately 50 mg of fat samples were precisely weighed into 20 mL capacity glass ampules. A volume of 0.1 mL of the hexane solution of the internal standard (heptadecanoic acid at a concentration of 10 mg/mL) was introduced to the fat sample [25 ]. The procedures for fat saponification and fatty acid esterification were conducted following previously established methodologies [26 (link),28 ,50 ].
Gas chromatography (GC) was carried out using a Varian GC 450 gas chromatograph equipped with a flame-ionization detector (FID) and a 30 m (0.32 mm i.d.) column coated with a 0.25 µm film of SelectTM Biodiesel for FAME. A temperature gradient was applied (200 °C for 10 min, then incremented by 3 °C/min to 240 °C, holding at 240 °C for 5 min). The injection port and detector temperatures were set at 250 °C and 300 °C, respectively, with a split ratio of 1:50. The flow rates were adjusted to achieve a ratio of gas flows (column + carrier gas):(detector supply):(air) at 1:1:10, with carrier gas (helium) at 28 mL/min, detector supply (hydrogen) at 30 mL/min, and detector supply (synthetic air) at 300 mL/min.
Quantitative analysis relied on calibration curves established for FAMES standard mixture (C14–C22) within the concentration range of 0.1–80.0 g/100 g.
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