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Elemental analyzer

Manufactured by Eurovector
Sourced in United Kingdom

The Elemental Analyzer is a laboratory instrument designed to determine the elemental composition of a wide range of organic and inorganic materials. It provides rapid and accurate analysis of the carbon, hydrogen, nitrogen, sulfur, and oxygen content of samples.

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6 protocols using elemental analyzer

1

Stable Isotope Analysis of Organic Samples

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In order to determine the δ13C values, the samples (0.060 mg) were loaded into zin capsules and combusted at a temperature of 1100 °C, and then, CO2 was separated in gas chromatography column in the elemental analyzer (EuroVector). In order to determine the δ18O values, the samples (0.095 mg) were loaded into silver capsules. To displace moisture-containing air in the glucose samples, the samples were heated over 24 h in a vacuum line (60 °C), and after that, they were put into a special air-filled homemade dry box before stable isotope ratio determination (Sensuła et al. 2011b (link)). The samples were converted to CO by pyrolysis at a temperature of 1350 °C and separated in gas chromatography column in the elemental analyzer (EuroVector).
The stable oxygen and carbon isotope compositions of the samples were determined using an Isoprime continuous flow isotope ratio mass spectrometer (GV Instruments, Manchester, UK) at the Mass Spectrometry Laboratory of the Silesian University of Technology.
The relative deviation of the isotopic composition is expressed, in parts per thousand (‰), as δ=(Rsample/Rstandard1)×1000,
where Rsample and Rstandard are the ratios of the heavy to the light isotope concentration in the sample and in the standard, respectively. The δ13C results are reported in values relative to VPDB, whereas the δ18O results are reported in values relative to VSMOW.
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2

Carbon Isotope Analysis of Plant Samples

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δ13C values, a measure of the carbon isotope composition, were determined at Washington State University on leaf samples taken from plants using a standard procedure relative to PDB (Pee Dee Belemnite) limestone as the carbon isotope standard (Bender et al., 1973 (link)). Plant samples were dried at 80 °C for 24 h, milled to a fine powder and then 1–2 mg were placed into a tin capsule and combusted in a Eurovector elemental analyzer. The resulting N2 and CO2 gases were separated by gas chromatography and admitted into the inlet of a Micromass Isoprime isotope ratio mass spectrometer (IRMS) for determination of 13C/12C ratios. δ13C values were calculated where δ13C=1000×(Rsample/Rstandard)–1, where R=13C/12C.
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3

Crab Trophic Position and Size

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I assessed individual long‐term diet variation using stable nitrogen isotope values that have previously been used to examine the correlation between relative trophic position and reproductive success (Griffen 2014). Here, I use these same data to examine the relationship between crab size (carapace width, CW) and relative trophic position, which has not previously been explored. δ15N values generally increase with trophic position and can therefore accurately be used to assess relative trophic position between individuals (Post 2002). δ15N values were obtained from muscle tissue taken from a single walking leg of each crab and were measured using an Isoprime mass spectrometer connected via continuous flow to a EuroVector Elemental Analyzer. Three internal standards were run approximately every 40 samples to calibrate the system and to compensate for potential drift over time (USGS40, N1 and N2). I tested the hypothesis that relative trophic position would increase with crab size using a linear model with δ15N as the response variable and crab CW as predictor variable.
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4

Carbon Isotope Ratio Analysis

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Approximately 0.01 m of the tips of both branches of the second vegetative flush were dried in an air forced ventilation oven at 65°C for 72 h, ground in a mill grinder (Willy–MSSL-031). Thereafter, a range of ca. 2 mg of sample were weighed out in tin capsules. Thereafter, the carbon (13C/12C) isotope ratio of the samples was analyzed in an Isoprime isotope ratio mass spectrometer (Micromass, Wilmslow, United Kingdom) coupled to an elemental analyzer (Eurovector, Pavia, Italy). Isotopic C-ratio was calculated using the following standard δ notation:
where R = 13C/12C for carbon. The isotope ratios were calibrated against the international standards IAEA CH6 and IAEA CH7. δ13C results were referenced against Pee Dee Belemnite (PDB). Precision (the standard deviation of the set of standards analyzed in each batch) was 0.06‰.
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5

Characterizing Leaf Litter Chemistry

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Leaf litter was collected in late September 2017. We collected senescent leaves of dwarf shrubs which were still attached to the plants, and samples of brown moss (three replicate samples per plant species). While leaf litter accounts for only a minor proportion of total vascular plant litter mass, it generally exhibits higher variation in chemical quality among plant species compared to root litter (Hobbie 1996 (link); McLaren et al. 2017 (link)). Samples of green leaves and green moss (three replicates) were collected in mid-growing season (end of July). All leaf and litter samples were dried at 60 °C and ground in a ball mill.
Total C and N in leaf and litter samples were determined by an elemental-analyzer (Eurovector). A characterization of chemical quality of litter samples was obtained using Fourier transform near-infrared (FT-NIR) spectroscopy, as described above for soil samples. Concentrations of condensed tannins in leaf litter were determined using the protocol described above for soil samples.
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6

Stable Isotope Analysis of Soil C and N

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Soil samples were dried (0.5 mg) and acidified (1% HCl) in tin or silver boats to remove inorganic carbon. Samples were combusted in a Eurovector elemental analyzer and resulting N2 and CO2 gases were separated by gas chromatography and admitted into an IRMS mass spectrometer for determination of 15N/14N and 13C/12C ratios (reproducibility: 70.5% for d15N and 70.2% for d13C). C-isotopic ratios were measured against a Pee Dee Belemnite (PDB) standard for δ13C and atmospheric nitrogen for δ15N. Results are expressed as delta (δ) notation, where δX (‰) = [(Rsample/Rstandard) − 1] × 103, where R = 15N/14N or R = 13C/12C.
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