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42 protocols using 5100 icp oes

1

Quantification of Trace Elements in Vaginal Fluid

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The zinc and copper concentrations of the pre-treated fluid samples were measured by inductively coupled plasma optical emission spectrometry (ICP-OES 5100, Agilent Technologies, USA). The measurements were conducted in SVDV (Synchronous Vertical Dual View) mode, gaining intensity data from the axial and radial view, simultaneously. We applied an automatic sample introduction (SPS 4, Agilent Technologies, USA), and measured the samples in a randomized design. We performed measurements to generate a five-point calibration curve for the quantitative analysis of copper and zinc. Calibration solutions were diluted from a multi-element standard of 1000 mg/L (ICP standard IV, Merck, Germany) with 0.1 M nitric acid in ultrapure water. We expressed the trace element concentration of vaginal fluid samples in mg/L. The operating parameters of ICP-OES are described in Table 1.

The operating parameters of ICP-OES 5100 (Agilent Technologies)

ICP-OES operating parameters
Repetition3
Pump speed15 rpm
Uptake time20 s, fast pump
Rinse time30 s, fast pump
Read time10 s
RF energy1.20 kW
Stabilization time7 s
View modeSVDV
view height0 mm
Nebulizer gas0.70 l/min
Plasma gas12.0 l/min
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2

Trace Element Analysis of Tissue and Blood

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The elemental analysis of the pre-treated tissue and blood samples was carried out by inductively coupled plasma optical emission spectrometry (ICP-OES 5100, Agilent Technologies, Santa Clara, CA, USA). The measurements were conducted in SVDV (Synchronous Vertical Dual View) mode, gaining intensity data from the axial and radial view, simultaneously. An automatic sample introduction was applied (SPS 4, Agilent Technologies, Santa Clara, CA, USA), and the samples were measured in a randomized design [20 (link)]. We have performed measurements to generate a five-point calibration curve for the quantitative analysis of copper and zinc. We have diluted the calibration solutions from a multi-element standard of 1000 mg/l (ICP standard IV, Merck, Germany) with 0.1 M nitric acid in ultrapure water. We have expressed trace element concentration of vaginal tissues in milligrams per kilogram (mg/kg), and trace element concentration of whole blood samples in milligrams per liter (mg/l) [20 (link)].
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3

Copper Removal from Aqueous Solutions

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The prepared samples, in powder form, were dispersed in water and kept in contact with a solution of CuCl2 (10 mg L−1) at room temperature. The tests were performed in the presence of 2.5 g L−1 of adsorbent samples under stirring and at a working pH of 4.5. To quantify the sorption, after keeping the samples in contact with Cu2+, 8 mL were centrifuged at 4500 rpm for 40 min by ultrafiltering the sample with centrifugal filter units (Polyethersulfone, Amicon filter 5 KDa, Millipore, Burlington, MA, USA). In this way, we separated the powder samples from the solution and quantified them via inductively coupled plasma atomic emission spectroscopy coupled with a OneNeb nebulizer (ICP-OES 5100—vertical dual view apparatus—Agilent Technologies, Santa Clara, CA, USA); the non-absorbed Cu2+ remained part of the solution despite the increase in time (1 and 24 h). The analyses were performed in radial viewing mode, and calibration curves were obtained with 0.1, 1.0, 10.0, and 100.0 mg L−1 standards for the element. Nitric acid was added to standards and diluted samples (1:10 v/v). The calibration curve was evaluated and showed a good correlation coefficient (R2) above 0.99. Results from ICP-OES were reported as the average of three independent measurements with relative standard deviation.
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4

Co Loading Determination of CoO/SiO2 Catalyst

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The Co loading of the SiO2 supported CoO nanoparticles
was determined by ICP-OES performed by Galbraith Laboratories (Knoxville,
TN). The Co loading of the calcined IWI-Co/SiO2 catalyst
was determined by ICP-OES at NREL. Around 250 mg the solid material
was mineralized in a Teflon tube with 2 mL of concentrated HNO3, 1 mL of concentrated fluoroboric acid, and 5 mL of concentrated
hydrochloric acid using a microwave digestion system (UltraWAVE 2,
Milestone) at 1500 W following the UW-GE-4 method provided by Milestone.
The sample was then diluted to 50 mL with distilled water with 0.25
mL of 1000 ppm yttrium in 2% HNO3 (Accustandard; New Haven,
CT) added to serve as an internal standard for analysis by ICP-OES
(ICP-OES 5100; Agilent Technologies Inc.).
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5

Leaf Nutrient Analysis and Orchard Mapping

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Twenty mature healthy leaves from the canopy of two trees per plot were sampled on May 27, 2020, a week after the major heatwave ended. The leaves were dried at 70 °C in a well-ventilated oven. Then, each sample was ground and thoroughly mixed. The quantity of Cl in the leaf was determined based on water extraction (0.1 g dry matter in 10 mL deionized water), using an MKII Sherwood M926 Chloride Analyzer. Na and Ca were determined by digesting the powdered material with nitric acid and H2O2 and analyzed using ICP-OES 5100 (Agilent Technologies). In addition, the orchard was mapped from a drone, using an RGB camera (SONY ILCE-600); the procedure that was used with the thermal camera, described above, was followed.
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6

Comprehensive Biochemical Analysis of Samples

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Biochemical analysis was carried out on the 32 samples. The dry matter (DM) content of collected samples was determined by oven-drying at 105 °C to a constant weight.
After extraction in petroleum ether, the lipid content was determined after acid hydrolysis using the semi-automatic 2055 Soxtec system (Foss, Nanterre, France) according to the 2003.05 and 2003.06 AOAC procedures [16 (link)].
Protein content (N × 6.25) was determined by the method of Kjeldahl (ISO 1871:2009).
Mineral contents were analyzed by inductively-coupled plasma optical emission spectroscopy using an ICP-OES 5100 (Agilent Technologies, Les Ulis, France) after wet mineralization of 0.4 g sample in H2O2 and concentrated HNO3 (1/7; v/v) in an Ethos 1 microwave digester (Milestone, Sorisole, Italy).
All analyses were done in duplicate and values were averaged.
Data management and statistical analysis: Survey data were captured in an Excel spreadsheet and then checked carefully. Responses to open-ended questions were grouped and coded according to the main trends and ideas. SPSS Software (IBM corporation, Chicago, United States of America) was then used for descriptive analysis.
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7

Sediment Sampling and Heavy Metal Analysis

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A shallow sediment (0–2 cm deep) sample was collected from each sampling point at each sampling time using a Van Veen grab sampler. Each sample was immediately packed in an airtight polythene bag and stored at – 20 °C prior to analysis. For heavy metal analysis, sediment samples were dried and then digested with analytical grade reagents following a method described by Kouadia and Trefry79 . The Cd, Cr, Co, Cu, Fe, Pb, Mn, Ni, and Zn concentrations in the digest were then determined by inductively coupled plasma optical emission spectrometry (ICP-OES 5100, Agilent Inc.). The total organic carbon (TOC) content of each sample was determined using a Shimadzu TOC 5000 automatic analyser (Shimadzu, Kyoto, Japan). Measurement of all samples was carried out in duplicate.
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8

Quantitative Lead Analysis by ICP-OES

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The concentration of Pb2+ was assessed using an inductively
coupled plasma optical emission spectrometer (Agilent ICP-OES 5100,
Australia) based on the standard method (APHA, 2017). For three replicates,
the relative standard deviation was less than 1%.
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9

Multianalyte Water Quality Analysis

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Dissolved Fe2+ and Mn2+ concentrations were measured by Inductively Coupled Plasma-Optical Emission Spectroscopy (ICP-OES 5100, Agilent Technologies (72 )). Concentrations of NH4+ (73 ), NO3 and NO2 (74 (link)), and H2S (75 ) were determined photometrically on a plate reader (Synergy HT, BioTek). Concentrations of SO42– and Cl were measured by Ion chromatography (DIONEX DX-320 (72 )). Standards consisted of solutions of MilliQ water containing analytical-grade ammonium chloride, zinc sulphide, and sodium salts of sulfate, chloride, nitrate, and nitrite, and an ICP-multielement standard solution (all Sigma-Aldrich, Switzerland).
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10

Elemental Composition Analysis of Seed Mutants

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Mature F4 seeds of the selected mutant lines along with controls (cv. Kronos and WT sibling lines) were grounded to fine powder and oven-dried at 80°C to constant weight. Samples were introduced in polypropylene tubes (digiTUBES, SCP Science, Champlain, NY, USA) with 3 mL of concentrated nitric acid and 1 mL of concentrated hydrogen peroxide and heated in a block system (DIGIPREP, SCP Science, Champlain, NY, USA) for 120 min at 95°C. After digestion, the extracts were filtered by a 0.45 μm teflon filter (DigiFILTER, SCP Science, Champlain, NY, USA). After cooling down, the digests were diluted with dH2O and analyzed by inductively coupled plasma-mass spectrometry (ICP-MS 7900, Agilent Technologies, Santa Clara, CA, USA) with Octopole Reaction System (ORS). Phosphorous and sulfur in the digested solutions were determined by inductively coupled plasma-optical emission spectrometer (ICP-OES 5100 Agilent Technologies, Santa Clara, CA, USA). Data have been expressed as mean values of three biological replicates ± standard error. Three technical replicates were carried out for each biological replicate. The ICP-MS operating conditions are summarized in Supplementary Table S2.
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