Triplus autosampler
The TriPlus autosampler is a laboratory instrument designed to automate the sampling and introduction of liquid or solid samples into an analytical instrument, such as a gas chromatograph or a liquid chromatograph. The core function of the TriPlus autosampler is to precisely and consistently deliver samples for analysis, ensuring reproducible and reliable results.
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15 protocols using triplus autosampler
Fatty Acid Profiling of Implant Samples
Headspace-SPME-GC-MS Analysis of Coffee Volatiles
GC-MS Analysis of Derivatized Samples
Each 1 μL aliquot of the derivatized sample solution was injected in splitless into the GC column by a TriPlus autosampler (Thermo Fisher Scientific), at a constant flow rate of helium of 1 mL·min−1. The temperature of the injector was operated isothermally at 280 °C. The mass spectrometry (MS) transfer line temperature to the quadruple was set to 150 °C and the electron impact (EI) ion source ion temperature was 230 °C. Compound elution settings were 2min at 80 °C isothermal, followed by a 10 °C∙min−1 oven temperature gradient to a final 325 °C, and then hold for 6 min at 325 °C. The system is then temperature equilibrated for 1 min at 80 °C before injecting the next sample. Ions were generated by a 70 eV electron beam. The spectra were recorded with a scanning range of 50–550 m ∙ z−1.
Optimization of SPME-GC/MS Analysis for Chimonanthus praecox Floral Fragrance
GC-MS Analysis of Derivatized Samples
Determining 13C Enrichment in Biomarkers
GC-MS Analysis of Derivatized Samples
For the mass spectrum the positive electron ionization (+ EI) mode at electron energy of 70 eV with a solvent hold-up of 7 min was followed for the operation. A full-scan mode from m/z, 45–800 was used for the operation of mass spectrum. MS library NIST v. 1.0.0.12 was used to detect and identify the organic compounds.
Soil Chemical Properties and PAHs Analysis
The content of 16 PAHs was determined with the Trace GC/MS Ultra ITQ900 system with a TRIPlus autosampler (Thermo Fisher Scientific, Waltham, MA, USA) and a flame ionization detector. The total content of 16 PAHs (naphthalene, acenaphthene, acenaphthylene, fluorene, phenanthrene, anthracene, fluoranthene, pyrene, benzo(a)anthracene, chrysene, benzo(b)fluoranthene, benzo(k)fluoranthene, benzo(a)pyrene, indeno(1,2,3-cd)pyrene, dibenzo(a,h)anthracene and benzo(g,h,i)perylene) was determined by the method described by Krzebietke et al. [3 (link)]. The content of LMW PAHs (naphthalene, acenaphthene, acenaphthylene, fluorene, anthracene, phenanthrene, fluoranthene, pyrene and chrysene) and HMW PAHs (benzo(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, benzo(g,h,i)perylene, indeno(1,2,3-cd)pyrene and dibenzo(a,h)anthracene) was determined in soil samples.
High-resolution GC-HRMS for PCDD/Fs and DL-PCBs
Quantification of 4MMP in Wine Samples
The GC was equipped with a J&W DB-WAX (60 m × 0.25 mm × 0.25 µm) column (Agilent, Santa Clara, California, USA). The carrier gas was helium with a constant flow rate of 1.2 mL/min, and the injector temperature was set at 250 °C. Injection was performed in splitless mode for 3 min and then operated at a split of 1/20. The source and transfer line temperatures were set at 250 °C. Ionization was performed by positive electronic impact (EI) at 70 eV, with argon being used for the second fragmentation.
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