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Famq 005

Manufactured by AccuStandard
Sourced in United States

The FAMQ-005 is a laboratory instrument designed for measuring the concentration of analytes in liquid samples. It utilizes a fluorescence-based analytical technique to detect and quantify the presence of specific compounds within the sample. The device is capable of performing various analytical tasks, but a detailed description of its intended use or specific applications is not provided.

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6 protocols using famq 005

1

Fatty Acid Profiling via Gas Chromatography

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Fatty acids were converted to their respective methyl esters (FAMEs) with the one-step in situ transesterification method of Indarti et al., as modified by Levine et al. [57 (link),58 (link)], and subsequent analysis was made on a GC (Agilent Technologies, 7890A) equipped with a detector (FID) and a capillary column (DB–WAX, 10 m × 0.1 mm × 0.1 μm), as previously described [59 (link)]. To quantify the produced FAMEs, a reference standard (FAMQ-005, Accustandard) and an internal standard solution (C17: 0, Sigma) were used [59 (link)].
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2

Characterization of Diesel-Biodiesel Blends and Soil Contamination

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Four diesel products, blended with biodiesel, were obtained from gas stations operated by four major oil refineries in Korea, and the samples were designated as D1, D2, D3, and D4. The diesel samples were stored in amber glass bottles with screw caps at 4 °C. The FAME composition in each diesel sample was determined by dissolving an aliquot of diesel in dichloromethane (DCM, ≥ 99%, JT Baker), analyzing by gas chromatography-mass spectrometry (GC–MS, QP 2010, Shimadzu), and comparing with the FAME standard (FAMQ-005, AccuStandard). We collected soil in the hillside near the Korea Institute of Science and Technology (KIST); this region is not exposed to petroleum products. The distribution of soil particle size was determined by sieve separation. The abundant particle size range of the soil was 2–0.075 mm, which belongs to sand; in addition, approximately 25 wt% of soil particles were below 0.075 mm, indicating the presence of silt and clay particles. The collected soil was dried for 7 days at room temperature, passed through a 2 mm mesh size sieve, and then used to prepare diesel-contaminated soils9 .
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3

Quantification of Fatty Acid Metabolites

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Cells were washed thrice by pre-cooled phosphate-buffered saline and fixed with methanol, put periodically twice from − 80 °C for 30 min to room temperature for 15 min, harvested by cell scraper and stored at − 80 °C until the analysis was conducted. FAs metabolites were measured essentially as described previously [42 ]. The relative abundances of the species in the sample-extracts was determined using a gas chromatography system coupled to a mass spectrometer (GC–MS-QP2010 Ultra, Shimadzu, Kyoto, Japan). Heptadecanoic acid was added as an internal standard and thirty-seven mixed Fatty Acid Reference Standard (FAMQ-005, AccuStandard, New Haven, USA) as an external standard. The thirty-seven metabolites were identified by their corresponding chemical standards. Data were analyzed using GCMSsolution software Ver.4.
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4

Lipid Profiling by In-Situ Transesterification

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Lipid content and the lipid profile were determined with one-step in-situ transesterification [43 (link)] and subsequent analysis of the derived Fatty acid methyl esters (FAMEs) was made on a GC (7890A, Agilent Technologies Inc., Santa Clara, CA, USA), equipped with a flame ionization detector (FID) and a capillary column (DB–WAX, 10 m × 0.1 mm × 0.1 μm) as previously described [44 (link)]. To quantify the produced FAMEs, a reference standard (FAMQ-005, Accustandard, New Haven, CT, USA) and an internal standard solution (C17: 0, Sigma-Aldrich, St. Louis, MO, USA) were used [44 (link)].
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5

Fatty Acid Profiling via GC-FID

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FAME samples were analyzed by injecting 1 µL of the FAME sample into the GC-FID. Hydrogen was used as the carrier gas at a flow rate of 1 mL/min and a split ratio of 30:1. FAME separation was achieved on a BPX-70 (0.32 mm; film thickness 0.25 µm, length 50 m) silica column (Phenomenex, Torrance, CA, USA). The initial column temperature was 100 °C, which was increased to 160 °C at a rate of 10 °C/min, and then up to 220 °C at a rate of 3 °C/min. This temperature was maintained for 5 min, and then increased to 260 °C at a rate of 10 ºC/min, and then held for a further 5 min. The retention times of 37 fatty acid methyl esters were determined using commercial FAME standards (FAMQ-005, AccuStandard, Inc., New Haven, CT, USA), which were analysed by GC-FID under identical running conditions. Docosapentaenoic acid (DPA) and several unknown peaks were identified based on the reported literature [5 (link),6 (link),7 (link),8 (link)].
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6

GC-MS Analysis of Fatty Acid Methyl Esters

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We injected 1 µl of each FAME solution in an Agilent Technologies 6890N GC Network System with a 7683 series injector and coupled to an electronic impact-mass spectrometry detector (EI-MS; 5973N MSD; Agilent Technologies). The capillary column used was a BPX70 column (30 m × 0.25 mm i.d., 0.25 µm film thickness; SGE Analytical Science). The injector in split mode (20:1) was set at a temperature of 270°C and the oven was maintained for 5 min at 100°C after injection and then increased to 240°C at a ramp rate of 2.5°C/min. The carrier gas was helium at a flow rate of 1.2 ml/min. The source inlet of the mass spectrometer was held at 230°C and 70 V. The identification and quantification of FAMEs was achieved by comparison to retention times of FAME reference standards (FAMQ-005, AccuStandard, New Haven, USA) and other FAMEs identified before in liver, testis and sperm samples with the same analytical method (Reglero et al., 2009 (link); Castellanos et al., 2010 (link)), and by their mass spectra. Calibration curves were performed with FAMEs concentrations ranging from 0.06 ng/µl to 11.89 ng/µl. Blanks were processed with each batch of samples.
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