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28 protocols using agilent 7800 icp ms

1

ICP-MS Analysis of Trace Elements

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For small volume LC analysis (Agilent Infinity II coupled to Agilent 7800 ICP-MS), the following instrument parameters were used: RF power 1550 V, RF matching 1.00 V, nebulizer gas 0.99 L/min, option gas 0.0%, nebulizer pump 0.30 rps, S/C temp 2 °C, makeup gas 0.00 L/min, extract 1 lens 0.0 V, extract 2 lens −195.0 V, omega bias −95 V, omega lens 8.4 V, cell entrance −40 V, cell exit −60 V, deflect 0 V, plate bias −55 V, He flow rate 4.0 mL/min, octupole bias −18 V, octupole RF 200 V, and energy discrimination 3.0 V.
For large volume analysis (Agilent SPS 4 coupled to Agilent 7800 ICP-MS), the following instrument parameters were used: RF power 1550, RF matching 1 V, nebulizer gas 1.00 L/min, option gas, 0.0 %, nebulizer pump 0.10 rps, S/C temp 2 °C, makeup gas 0.00 L/min, extract 1 lens 0.0 V, extract 2 lens −200.0 V, omega bias −105 V, omega lens 7.5 V, cell entrance −40, cell exit −60 V, deflect −0.6 V, plate bias −55 V, He flow rate 4.5 mL/min, octupole bias −18.0 V, octupole RF 200 V, and energy discrimination 5.0 V.
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2

Quantifying Cellular Uptake of MnO2@PA NPs

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To evaluate the cellular uptake behavior of MnO2@PA NPs, cells were incubated with MnO2@PA NPs for 24 h. After incubation, cells were digested with trypsin and centrifuged at 1000 rpm for 5 min. The collected cells were washed and centrifuged. The centrifuged cells were re-suspended in 2 mL of DMEM medium and the number of cells were counted by inductively coupled plasma mass spectrometry (ICP-MS) (Agilent ICP-MS 7800, Agilent, USA) to determine the contents of manganese in the cells.
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3

Comprehensive Characterization of Vanadium-Containing Solid Residues

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X-ray diffraction (XRD, Brucker D8 Advance, Brucker, Germany) analysis were performed to determine the minerals of the raw VS and the leaching residues. The morphology and element distribution of the raw VS and the leaching residues were detected by a field emission-scanning electron microscopy coupled to an energy dispersive spectrometer (FESEM-EDS, SU8020, Hitachi, Japan). Using the Mastersizer 3000 laser particle size analyzer, the PS of the leaching residues was detected. The pore volume and specific surface area of the leaching residues were measured using the ASAP 2460 surface area analyzer. V concentration of the sampled leachate was determined using inductively coupled plasma massspectrometry (ICP-MS, Agilent ICPMS7800, Agilent, USA) analysis. The leachate pH and Eh were determined by pH and Eh meters. The Eh-pH diagram of V-H2O system at 25 °C was obtained using HSC software based on the basic thermodynamic data. The ultraviolet visible (UV–vis) absorption spectra of the obtained leachates were determined using the UV-3600 double-beam spectrometer (Shimadzu, Japan).
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4

Sb(V) Sorption Behavior at Varying pH

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The effect of pH on Sb(v) sorption on the materials was examined over the pH range from 1 to 11. Batch samples were prepared using 2 g L−1 adsorbent concentration, and 10 mg L−1 (0.082 mmol L−1) Sb(v) in 0.01 M NaNO3 solution. The pH of the solution was adjusted with a small amount of either NaOH or HCl. The samples were equilibrated for 24 h before phase separation that was carried out by centrifugation at 2100g for 10 min followed by syringe filtration (Acrodisc LC 0.2 μm PVDF). Equilibrium pH values were determined after the phase separation. Sample aliquots were taken and diluted with an acid mixture of HCl and HNO3 for Sb concentration measurement with an Agilent 7800 ICP-MS.
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5

Measuring Boron Uptake in Xenopus Oocytes

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Oocytes expressing TrAqps or water‐injected control oocytes were placed in ND96 containing 10 mM boric acid for 10 min at 23°C. Each oocyte was washed with ND96 for several seconds and dried after the removal of the washing solution. Dried Xenopus oocytes were digested with concentrated nitric acid in Teflon tubes, and the residues were dissolved in 0.08 M nitric acid containing 5 μg/L Be. Concentrations of boron‐10 and boron‐11 were measured by ICP‐MS (Agilent 7800 ICP‐MS, Agilent Technologies) using Be as an internal standard, and the sum of boron‐10 and boron‐11 concentrations is presented as the B concentration (Takano et al., 2006 (link)).
Quantitative data of oocytes from at least three frogs are presented as the mean ± SEM. Values for B content were compared among oocytes expressing TrAqps and control oocytes, and the statistical significances (p values) were calculated by one‐way analysis of variance (ANOVA) followed by Dunnett's test using GraphPad Prism software.
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6

Caco-2 Transwell Zinc Uptake Assay

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0.5 mL Caco-2 cells were seeded into the upper chamber in 12-well transwell dishes (Corning Costar Co., Cambridge, MA) at a density of 2 × 105 cells per mL in serum-containing DMEM and 1.5 mL serum-containing DMEM was added to the lower chamber. Each medium was changed the other day, and every day after seven days. The monolayers' transepithelial electric resistance (TEER) was determined using the Millicell ERS-2 system (Millipore Corp., New Bedford, MA, USA). Experiments on zinc uptake were conducted when the cells had TEER values over 1000 Ω cm2.
The assay was performed after Caco-2 cells were incubated for one hour with DMEM containing 2% FBS. The cells were then washed three times with Dulbecco's–Hanks balanced salt solution (D–Hank's). Then, add 0.5 mL samples (the final concentration of ZnSO4 is 40 μM, and the final concentration of α-La, β-LG, and BSA is 1%) to the upper chamber and 1 mL D–Hank's to the lower chamber. Each group was set up with three replicates. After 2 h incubation in the incubator, the lower chamber samples were collected and cleaned once with 0.5 mL D–Hank's and combined. The zinc content was detected by inductively coupled plasma mass spectrometry (ICP-MS, Agilent 7800 ICP-MS, USA).
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7

Wheat Husk Characterization by FTIR and ICP-MS

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The surface chemistry and absorption bands of functional groups of fresh wheat husk and its ash powder are examined by Fourier transform infrared spectroscopy (Brucker, VERTEX 70, Germany) in the range of 500 to 4000 cm−1. The chemical compositions of wheat husk ash are detected using an Inductively Coupled Plasma-Mass spectrometry (Agilent 7800 ICP-MS, Japan).
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8

Elemental Analysis of Plant Shoots

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Shoots were harvested, dried at 60°C for 48 h, and digested with HNO3 and H2O2 at 100°C. Digested samples were dissolved and diluted with 0.08 M HNO3 and analyzed using inductively coupled plasma-mass spectrometry (Agilent 7800 ICP-MS; Agilent Technologies, Santa Clara, California, USA). All experiments were conducted with three independent biological replicates.
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9

Platinum complex stability in buffered serum

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Fetal calf serum was purchased from Sigma-Aldrich and buffered with 150 mM phosphate pH 7.4 in order to guarantee a stable pH. The platinum(iv) complexes (5 mM) were dissolved in 150 mM phosphate buffer (pH 7.4) and diluted 1 : 50 in the buffered serum to obtain a final concentration of 100 μM. The samples were then incubated in the autosampler at 37 °C and analyzed every 1 h for 6 h. Between each sample a pure water blank was measured. For SEC-ICP-MS measurements an Agilent 1260 Infinity system coupled to an Agilent 7800 ICP-MS equipped with a dynamic reaction cell was used. Oxygen (purity 5.5, Messer Austria GmbH, Gumpoldskirchen, Austria) was used as reaction gas. HPLC parameters are given in Table S2 and ICP-MS operation parameters are given in Table S3.
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10

Trace Metal Analysis in Biological Samples

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The target elements were eight essential trace metal elements (chromium [Cr], manganese [Mn], iron [Fe], cobalt [Co], copper [Cu], zinc [Zn], selenium [Se], and molybdenum [Mo]) in medium and lysate, and Mn and Zn in urine and serum.
All elements were measured by inductively coupled plasma mass spectrometry (ICP-MS; Agilent 7800 ICP-MS, Agilent Technologies, California, USA). The reagents used were nitric acid 1.38 (Kanto Chemical, Tokyo, Japan) and ICP-MS mixing standard XSTC-622 (SPEX CertiPrep, New Jersey, USA). Medium, lysate and urine were diluted 10-fold and serum was diluted 20-fold before analysis. (1 + 99) nitric acid was used as the diluent. For urine and serum, if they exceeded the calibration range, both were diluted 100-fold with (1 + 99) nitric acid. Equal amounts of yttrium standard solution (Kanto Chemical, Tokyo, Japan) were added to each test solution as an internal standard.
Since urinary concentrations of elements are affected by water intake, the amount of the element excreted in 24 h was evaluated. Urine specific gravity was determined using a digital urine specific gravity refractometer (UR-S, ATAGO, Tokyo, Japan), and 24-h excretion was calculated based on total urine volume and urine specific gravity. The 24-h excretion was normalized by body weight.
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