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.
Gc 450
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.
12 protocols using gc 450
Urinary Metabolite Quantification by GC-MS/MS
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.
GC-MS Analysis of Chemical Compounds
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.
Comprehensive Biogas Substrate Analysis
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.
Quantifying Bacterial Oxygen Consumption
Methanol Dehydrogenation Reaction Catalysis
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.
Methane Detection via Gas Chromatography
Triclosan Quantification in Urine Samples
Photocatalytic CO2 Reduction and Methanol Oxidation
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.
Analytical Methods for Lignocellulosic Biomass
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.
Fatty Acid Methyl Ester (FAME) Analysis
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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