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132 protocols using gc 14b

1

Measurement of Dinitrogen Fixation and Photosynthesis

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The dinitrogen fixation activity and leaf photosynthetic rate were determined at flowering stage in Experiment 1. The photosynthetic rate was measured on the upper most fully-expanded leaf using portable infrared gas analyzer (Model LI-6400, Licor Co. Ltd., NE, USA) between 10:30 a.m. and 12:30 p.m. While taking the measurements, the photosynthetic active radiation was adjusted at 1200 µmol m−2 S−1, the humidity was 65%, the leaf temperature was 28 ℃, and the ambient CO2 concentration was 350 mol L−1. Dinitrogen fixation was analyzed by measuring the reduction of acetylene to ethylene at flowering time as follows. Intact root systems were excised and gently separated from the soil. The root system and attached nodules were quickly placed in a 1000 mL glass bottle. The bottle was sealed with a rubber stopper and 100 mL of air in the bottle was replaced with acetylene. Samples were incubated at ambient laboratory temperatures. During the incubation periods, 0.3 mL of gas samples were extracted at 10 min and 1 hour and injected into a gas chromatograph (Shimazu GC-14B, Shimazu Co., Kyoto, Japan) fitted with a flame ionization detector to determine the ethylene concentration. Specific nitrogenase activity was calculated by dividing the nitrogenase activity of each sample by the dry weight of the nodules.
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2

Measuring Methane Emissions in Rice Fields

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The emission of CH4 was measured weekly or biweekly between 7 June and 23 August using a closed chamber method, as described previously (16 ). Each chamber consisting of lower (60 cm H) and upper (60 cm H) sections was placed over 4 hills of rice plants with a basal area of 30 × 60 cm. The upper section of the chamber fit over the lower one and was supported by a water-filled groove surrounding the outer top lip of the lower section, thereby providing an airtight seal between the two sections and surrounding atmosphere. Gas samples were collected from the chamber 0, 10, and 20 min after placement of the chamber. The samples were injected into pre-evacuated 19-mL glass vials and brought back to the laboratory for analysis. The mixing ratio of CH4 was determined by gas chromatography equipped with a flame ionization detector (GC-14B; Shimazu, Kyoto, Japan). The emission of CH4 was calculated based on an increase in the mixing ratio of the basal area of the chamber, chamber volume, and temperature inside the chamber. An analysis of variance (ANOVA) was conducted on the cumulative amount of CH4 that was emitted during 41–90 days after transplanting (DAT) using a general linear procedure. [CO2], temperature, and [CO2]×temperature were treated as fixed effects, while ring and ring×[CO2] were treated as random effects.
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3

Measuring Methane Emissions from Rice Paddy Fields

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We set an approximately 2 m long and 0.5 m wide ladders from the center of the shorter bund to allow measurement of CH
4 without touching the paddy soil surface. Those ladders were on the borders of the non-planted areas in each field. We set PVC chamber bases on the paddy fields of both sides of the ladders to avoid measurement perturbation. Chambers (60 × 80 cm and 100 cm high, transparent acryl) were set on a watertight chamber bases for every measurement. Measurements were taken at 8 a.m. because previous research has indicated that emissions at this time have a high correlation (ca. 90% of average emission) with average daily emissions
22 . We mixed the air in the chamber with a fan for 5 min after setting the chamber, then sampled the first gas, then sampled the second gas 20 min later. We conducted the measurements once a week throughout the rice growing stage, but every 3 days for 2 weeks after seeding, heading stage, and around draining. The samples were analyzed by gas chromatography (GC-14B, Shimazu, Kyoto). The cumulative CH
4 emissions were calculated by linear interpolation.
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4

Gas Production and Composition Analysis

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Fast of all, the gas production amount was measured by the water displacement method. A vial bottle containing the culture solution was placed in water, and a needle was pierced into the butyl rubber cap in the water to collect gas into a graduated cylinder. After the gas volume in the cylinder had been measured, the gas was transferred into a 10 mL vial bottle in water and stored sealed with a butyl rubber cap and screw cap. The components of the gas were measured using a gas chromatograph. A gas chromatograph GC-14B (Shimadzu Corporation, Kyoto, Japan) equipped with both thermal conductivity detector and flame ionization detector and a stainless column filled with Porapak Q (80–100 mesh) was used in this study. The column temperature was 100 °C and the flow rate of helium carrier gas was 30 mL/min. The pH was measured using a pH meter, LAQUA twin pH-22B (HORIBA, Ltd., Kyoto, Japan). Protein concentration of the culture solution was measured using TaKaRa Bradford Protein Assay Kit (Takara Bio Inc., Shiga, Japan) and a spectrophotometer UV-2450 (Shimadzu Corporation, Kyoto, Japan) in accordance with the instruction manual.
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5

Methane Production Analysis in Anaerobic Cultures

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The methane concentration in the headspace of the microcosms was analyzed by gas chromatography (GC) using a gas chromatograph model GC-14B with a flame ionization detector (FID) (Shimadzu, Kyoto, Japan) equipped with a 30-m 0.25-mm-ID 0.25-m-film-thickness Rtx-5 capillary column (Restec Col., Ltd., Bellefonte, PA, USA). Helium was used as the carrier gas. The analytical conditions have been previously described [53 (link)]. For methane analysis, 100 μL of the headspace of the anaerobic tubes was collected with a 500 μL gas-tight sample lock syringe (model 1750SL, Hamilton, NY, USA) through butyl rubber stoppers and injected into the gas chromatograph. Methane production [µmol] was calculated by converting peak areas of methane detected by GC analysis using an external standard curve as described previously [53 (link)]. Total carbon content in CH4 production [µg C] was calculated according to the following equation:
Total carbon content in CH4 production [µg C] = CH4 production [µmol] × 16.04 (molecular weight of CH4) × 12/16.04 (ratio of carbon content in CH4).
The conversion rate of TOC to methane was calculated according to the following equation:
Conversion rate [%] = Total carbon content in CH4 production [µg C] / TOC in 10 mL culture [µg C] × 100.
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6

Analytical Methods for Microbial Cultivations

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Acids (Acetic acid, butyric acid) and solvents (Ethanol, acetone, butanol) were analyzed with GC-FID (GC-14B, Shimadzu Inc., Kyoto, Japan) equipped with a ZB-FFAP column (Phenomenex Inc., Torrance, CA, USA). Glucose was measured with the Reflectoquant Glucose Test (Merck KGaA, Darmstadt, Germany). Optical density was obtained from a UV-VIS-spectrophotometer at a wave length of 600 nm. The cell dry mass was calculated from the OD 600 using the experimentally determined factor of 0.4 g L -1 OD 600 -1 [6]. For monitoring the morphology of cells and sterile control, a microscope (Axiostar plus, Zeiss, Göttingen, Germany) with 100× magnification was used. Sporadically the phosphate concentrations were measured along the cascade using the phosphate analysis method DIN EN ISO6878 2004/09.
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7

Comprehensive Lipid and Sterol Analysis

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Serum phospholipid, TG, cholesterol, high-density-lipoprotein (HDL) cholesterol, and non-HDL cholesterol were measured using an Olympus AU5431 automatic analyzer with AU reagent (Beckman Coulter Inc., Brea, CA, USA).
Total liver lipids were extracted according to the method of Bligh and Dyer (23 (link)). Each total lipid sample was dissolved in 2-propanol, and the TG content was determined using an enzymatic assay kit (Triglyceride E-Test Wako, Wako Pure Chemical Industries Ltd.). Liver cholesterol content was analyzed using a gas-liquid chromatography system (GC-14B, Shimadzu Co., Kyoto, Japan) equipped with a SE-30 column (Shinwa Chemical Industries, Kyoto, Japan) in which 5α-cholestane was used as an internal standard. Liver phospholipid content was measured by phosphorus analysis (24 (link)).
Feces were dried to a constant weight and then ground to a fine powder. Fecal fatty acid content was determined by the method of van de Kamer et al. (25 (link)). The level of fecal neutral sterol, including cholesterol and coprostanol, was determined by gas-liquid chromatography as described above. Fecal acidic sterol content was determined as micromoles of 3α-hydroxysteroid based on the molar extinction coefficient of NADH at 340 nm (26 (link)). Fecal nitrogen content was determined by the Kjeldahl method (27 (link)).
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8

Quantitative Analysis of Fermentation Broth

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The total residual sugars in the fermentation broth were measured using the phenol sulfuric acid method42 (link). The direct counting method was employed using a haemacytometer (H-0004, Boeco, Germany) with methylene blue staining to determine the viable yeast cell number43 . The ethanol concentration was determined by gas chromatography (GC) (Shimadzu GC-14B, Kyoto, Japan) using a polyethylene glycol (PEG-20 M)-packed column with a flame ionization detector, following the protocol described by Laopaiboon et al.44 (link). The ethanol yield (Yp/s, g/g), volumetric ethanol productivity (Qp, g/L.h), and conversion efficiency or yield efficiency (Ey, %) were calculated as described by Nuanpeng et al.45 (link).
All the experiments were performed in duplicate and repeated twice. The results were expressed as the means ± standard deviation (SD), and the mean differences between each treatment were analyzed by Duncan's multiple range test (DMRT) at a probability of p ≤ 0.05 using the SPSS program for Windows.
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9

Continuous Flow Alkylation of Benzene

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The alkylation of benzene with 1-dodecene was performed in a continuous-flow fixed bed micro-reactor (see Fig. S1) at 4.2 MPa, consisting of a stainless tube reactor with a length of 50 cm and a diameter of 1 cm. A typical experiment was performed using 1 g catalyst mixed with 10 g quartz sand. Before reaction, the catalyst was activated under 100 ml min−1 N2 flow for 3 h at 300 °C. After cooled to 100 °C, benzene was firstly pumped into the reactor to reach 4.2 MPa and then the mixture of benzene/1-dodecene with molar ratio of 15/1 (benzene/1-dodecene) was switched into the reactor. Different amounts of oxygenated organic compounds were added into the reaction mixtures where needed. It should be noted that all steps of the preparation of feedstocks was conducted in fume hoods. The effluent mixture was analyzed offline with a gas chromatograph (Shimadzu GC-14B) equipped with a flame ionization detector (FID). The catalyst was assumed to be deactivated as the conversion of 1-dodecene decreased below 95%, and then the lifetime was calculated thereof. It should be noted that B-fresh, B-heptanol, B-heptaldehyde, B-heptanoic acid and B-coke appearing in the following text represent the fresh beta zeolite, and the deactivated beta caused by n-heptanol, n-heptaldehyde and n-heptanoic acid and coke, respectively.
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10

Rice CO2 Flux Measurement Protocol

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The CO2 flux measurement was determined by the closed chamber method at four growth stages of rice cultivation. These growth stages were the jointing, heading, filling and maturing stages. In order to exclude the influence of photosynthesis, CO2 was sampled at night (the sampling lasted for one hour each time). The concentration of CO2 in the gas samples was analyzed using a gas chromatograph (GC- 14B, Shimadzu, Japan)20 and stable carbon isotopic ratios were measured using ThermoFinnigan/mat253 to estimate the fraction of respired CO2 that was derived from biochar.
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