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Hp 5890 series 2

Manufactured by Agilent Technologies
Sourced in United States, Germany

The HP 5890 Series II is a gas chromatograph designed for analytical laboratory applications. It is capable of separating and analyzing complex mixtures of chemical compounds. The core function of the HP 5890 Series II is to provide precise and reliable separation and detection of analytes in a sample.

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9 protocols using hp 5890 series 2

1

Gas Chromatography and Mass Spectrometry Analysis

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On 19 June 2013 and 20 August 2013, CH3Cl and CO2 mixing ratios were determined by GC (HP 5890 Series II, Agilent) using a Porapak Q 80/100 column (Supelco, USA) and a helium-methane mixture (95:5) as the carrier gas. On 16 July 2016, CH3Cl mixing ratios were determined by ISQTM Quadrupole mass spectrometer (MS) coupled with TRACETM Ultra gas chromatograph (GC) (Thermo Fisher Scientific, Massachusetts, USA). CH3Cl and CO2 mixing ratios were calculated by regression analysis based on a 5-point calibration with standard mixing ratios of both gases. In the SIP experiment, GC MS analysis (Perkin–Elmer GC Clarus 600 system) was carried out as described previously [22 (link)]. Further Details of gas analysis methods are given in Supplemental Information.
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2

Measuring N2 Production in Aquaculture

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To measure N2 production in an aquaculture setting, 40 common carp were divided over two 220 L metabolic chambers (90 × 60 × 45 cm) (total weight in tank 1: 1640 g, total weight in tank 2: 1730 g) and fed rations of approximately 1% body mass per day (Wageningen University, NL). As controls, two chambers without fish were used, one with tank water only and one supplemented with 100 µM NH4Cl. The chambers were sealed air-tight with lids and water locks. The air in the chambers was exchanged with a mixture of argon and oxygen (80%/20%) by flushing the chamber (8 L min-1, 1 h). After the removal of air, the gas phase in the chamber was circulated to secure dissolved oxygen levels (>4 mg L−1) in the water. As a control for leakages, 20 mL methane (CH4) was added to the gas phase of all chambers. 5 mL gas samples were taken every 15 min and water samples every 30 min for 240 min. Gas samples were analyzed with GC-MS as described above. CH4 was measured on a gas chromatograph equipped with a Porapak Q-column (100/120 mesh) and a flame ionisation detector (HP 5890 series II; Agilent Technologies, Santa Clara, CA, United States) with duplicate 100 µL injections. The ratio between N2 and CH4 was calculated for each chamber and normalized relative to the starting ratio.
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3

Trace-Level Contaminant Detection in Samples

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The final extracts were analyzed by gas chromatograph-agilent HP 5890 series II model equipped with auto sampler and Ni electron capture detector (ECD) that allowed the detection of contaminants even at trace level concentrations (in the lower μg/g and μg/kg range) from the matrix to which other detectors do not respond. The GC conditions used for the analysis were capillary column coated with VF-5 (30 m + 10 m EZ guard column × 0.25 mm internal diameter, 0.25 μm film thickness). The injector and detector temperature were set at 250 °C and 300 °C respectively. The oven temperature was programmed as follows: 60 °C held for 2 min, ramp at 25 ºC/ min to 180 °C, held for 1 min, and finally ramp at 5 °C/ min to 310 °C. Helium was used as carrier gas at constant flow rate of 1:4 °C / min and detector make-up gas of 29 mL / min. The injection volume of the GC was 1.5 mL with total run time for each sample was 31.4 min. Results obtained were presented as mg/kg concentration per analyte.
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4

Quantitative Analysis of Short-Chain Fatty Acids

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All samples were centrifuged and the supernatant was acidified by addition of ortho-phosphoric acid to obtain a final pH value of 2.0. Total VFA, i.e. C1–C6 short chain fatty acids, alcohols, lactic acid, and phenyl acetic acid, were determined gaschromatographically using an Agilent HP 5890 Series II gas chromatography system equipped with a flame ionization detector (FID) and a BP 21 bonded FFAP fused silica column (length 250 mm, diameter 0.53 mm, thickness of the immobilized phase 0.5 µm) [21 (link)]. The FID was used in the automatic and splitless mode. An automatic sampler injected 1 µl sample under the temperature program of 240/70–235/260 °C for injector, column and detector, respectively. H2 was applied as carrier gas with a H2-flow of 30 ml min−1. The air-flow of the FID was 300 ml min−1 with a makeup-flow of 25 ml nitrogen per min. The total run time was adjusted to 30 min. A weekly calibration was performed with a commercial external standard (Supelco 46975-U, Sigma-Aldrich, Germany). DM and VS content were determined according to the standard guidelines, i.e. VDI 4630 protocols [22 ].
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5

Quantification of Fecal Short-Chain and Branched-Chain Fatty Acids

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Concentrations of SCFA and BCFA were measured by gas chromatography at the German Institute of Human Nutrition Potsdam-Rehbruecke (DIfE), Nuthetal, Germany. The stool sample aliquot was weighed, diluted with 350 μL of water, and centrifuged (14,000× g, 5 min). The supernatant (100 μL) was mixed with 20 μL of 8.6 mM ethyl butyrate (internal standard), 280 μL of 0.36 M perchloric acid, and 270 μL of 1 M sodium hydroxide. After freeze-drying overnight, the residue was dissolved in 100 μL of 5 M formic acid and 400 μL of acetone and centrifuged (14,000× g, 5 min). An aliquot (1 µL) of the organic phase was used for the quantification of SCFA and BCFA by a gas chromatograph (HP 5890 series II; Agilent, Waldbronn, Germany) equipped with a HP-20 M column and a flame ionization detector (FID), as described previously [26 (link)].
Ammonia levels were determined at DIfE in fecal supernatants following ultrafiltration (Vivacon 500 centrifugal units, Sartorius, Göttingen, Germany) by using a colorimetric assay (Ammonia Colorimetric Assay Kit II, BioVision, Milpitas, CA, USA). Amounts of all compounds refer to fecal wet weight.
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6

Analytical Techniques for Wastewater Treatment

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The following parameters were measured daily on influent and effluent of both full-scale reactors: TOC was analyzed using a TOC analyzer (TOC-L CPN Basic System, Shimadzu, Japan). TSS was measured following the procedure of APHA (1998) [19 ]. For U1: Methanol and methyl acetate were detected using gas chromatography with FID on an HP5890 with a RTX-1 nonpolar column. Acetate is detected on a hp 5890 Series II with a DB-Wax polar column; and TA, BZ, IA, OA, PT, and TMA were detected using an Agilent 1200 HPLC System with multiple wavelength detector, or equivalent; the HPLC column was an Agilent SB-C18, 4.6 mm i.d. x 50 mm, 1.8 μm particle diameter (p/n 822975–902). For reactors E and F: TA, BZ, IA, OA, PT, and TMA were aromatic compounds, fatty acids and methyl compounds were detected using a high-performance liquid chromatography (Agilent ZORBAX Eclipse XDB-C18, Rapid Resolution HT 4.6 mm i.d. x50 mm, 1.8 μm particle diameter, operated at 600 Bar).
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7

GC-MS Analysis of Fatty Acid Methyl Esters

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The organic phases containing FAMEs were injected (0.5 μL) into a GC apparatus (HP5890 Series II, Agilent, Waldbronn, Germany) equipped with the column (100 m × 0.25 mm, 0.25 μm) CP-Select FAME (Varian, Palo Alto, CA, USA). The injector was kept at 270°C. To determine the whole profile of FAs, the oven temperature ramped from 135°C to 250°C (2.5°C/min) and was maintained at 250°C for 23 min. The same program was followed, starting from 160°C, when only LA and CLA had to be determined. Elution was performed with high-purity helium, with constant column head pressure of 200 kPa. Qualitative analyses of FAMEs were performed with a MS quadrupole detector (HP5972, Agilent). Analytes were identified by comparison with standards (O5632, Sigma Aldrich) and by analysis of their fragmentation patterns (EI, 70 eV) with the mass spectrum library NIST 2005 (Gatesburg, USA). Quantitative analyses were performed with a flame ionization detector held at 300°C.
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8

Quantification of Fatty Acids and FAMEs

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FFAs and FAMEs were extracted by addition of 6 mL of a 2:1 chloroform/methanol mixture (spiked with 0.15 mg/L of either methyl tridecanoate or methyl heptadecanoate as an internal control) to 5 ml of culture. For consistency in data analysis, 1 mL of dodecane layer was similarly treated with 6 mL of a 2:1 chloroform/methanol mixture before gas chromatography (GC) analysis. Quantification of FAs/FAMEs was conducted by GC-FID using an HP 5890 Series II gas chromatograph equipped with an HP-Innowax Column (0.32 mm x 30 m x 0.25 μm, Agilent). All samples were analyzed using the following parameters: inject: 1 μl; inlet temperature 250 °C with split ratio 1:1; carrier gas: helium; flow: 5 ml/min; oven temperature: initial temperature of 160 °C, hold 3 min; gradient to 255 °C at 5 °C/min; hold 3 min; inlet temp: 270 °C, detector temp: 330 °C. The amount of FAs/FAMEs was determined by comparison to a standard curve of various FAs and FAMEs and methyl tridecanoate or methyl heptadecanoate concentrations. To identify all FA/FAME products, GC/mass spectrometry analysis was additionally performed using an Agilent 6890-5975 equipped with HP-Innowax Column (0.32 mm x 30 m x 0.25 μm, Agilent). Peak identification was performed through comparison with GC retention time, known standards and mass spectra with the National Institute of Standards and Technology (NIST) database.
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9

Measuring Soil Carbon and Nitrogen Mineralization

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We measured soil C and N mineralization rates via the aerobic incubation method (Chen et al., 2019) . For each sample, 20 g of fresh soil was incubated in a 250-ml brown bottle at 25°C. During incubation, we added water to maintain the soil at 60% of field capacity based on weight. On incubation days 1, 2, 3, 7, 10, 15, and 21, we measured the CO2 released from the soil via gas chromatography (Agilent HP 5890 SERIES II, USA), and the average value was used as the soil C mineralization rate. NH + 4 -N and NO - 3 -N were extracted from a 20-g sample of fresh soil that was not incubated and a 20-g sample of incubated soil with 50 ml of 2 mol L -1 KCl; the contents of NH + 4 -N and NO - 3 -N were determined with a 2300 Kjeltec Analyzer Unit (FOSS, Höganäs, Sweden).
The difference in total inorganic N before and after incubation was the soil N mineralization rate.
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