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83 protocols using icap rq

1

Heavy Metal Analysis by ICP-MS

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Heavy metals ICP-MS analysis was performed with a Thermo Fisher Scientific iCAP-RQ equipped with nebulizer, a Teflon spray chamber and nickel (Ni) sampling cone, and platinum skimmer cone (Thermo Fisher Scientific, Waltham, MA, USA). The solutions were pumped by a peristaltic pump from tubes accompanied by an autosampler ASX-560 (ThermoFisher Scientific, Waltham, MA, USA). After the ICP-MS was stabilized for 20–30 min, the working ability was optimized daily with the tuning solution based on torch horizontal and vertical position, extraction lens, CCT (collision cell technology) focus lens and radio frequency power at 1550 W to minimize interference effects and to maximize signal. Highest purity argon and helium gas (99.99%) were used as the carrier gas in auxiliary flow at 0.8 mL/min, and nebulizer flow of 1.0 mL/min and 5.3 mL/min. For quantification, the analyte isotopes 82Pb, 48Cd, 33As and 50Sn were used.
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2

ICP-MS and ICP-OES Analysis Protocols

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The measurements were performed with the inductively coupled plasma mass spectrometer iCAP RQ (Thermo Scientific, Waltham, MA, USA) and the inductively coupled plasma optical emission spectrometer iCAP-7400 series (Thermo Scientific, Waltham, MA, USA). The data were acquired and processed with the ICP-MS Qtegra software (version 2.8.3170.309, Thermo Fisher Scientific, Waltham, MA, USA) and ICP-OES Qtegra software (version 2.8.2944.202, Thermo Fisher Scientific). The operating conditions of the devices, considering the specifics of the analyzed object, were studied using a MicroMist concentric nebulizer purchased from Glass Expansion (Melbourne, Australia).
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3

Comprehensive Exposure Biomarker Quantification

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Aliquots of urine samples were analyzed for exposure biomarkers at NSF International (Ann Arbor, MI), and extensive details on protocols have been previously described (Aung et al. 2019a (link); Ferguson et al. 2015b (link), 2017 (link); Kim et al. 2018 (link)). Quantification of exposure analytes were based on protocols and methods developed by the Centers for Disease Control and Prevention for use in the National Health and Nutrition Examination Survey. We measured 17 trace metals using a Thermo Fisher iCAP RQ inductively coupled plasma mass spectrometer with a Teledyne CETAC Technologies ASX-520 autosampler. We used isotope dilution liquid chromatography with tandem mass spectrometry (ID-LC-MS/MS) to quantify 8 PAH metabolites, 7 phenol-derived compounds, and 4 parabens. Finally, we quantified 9 phthalate metabolites using high-performance LC–electrospray ionization–MS/MS (HPLC-ESI-MS/MS). Figure 1 shows each exposure analyte according to its toxicant subclass and indicates abbreviations for each analyte. All exposure analytes that were below the limit of detection (LOD) were imputed by dividing the LOD value by the square root of 2.
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4

Comprehensive Characterization of Nanomaterials

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Ultraviolet-visible (UV-Vis) absorption spectra were collected using a UV2450 spectrophotometer (Shimadzu, Kyoto, Japan). Dynamic light scattering (DLS) and zeta potential were measured using the Zetasizer Lab Blue instrument (Malvern Panalytical, Malvern, Worcs, UK). Transmission electron microscopy (TEM) imaging was performed in a Hitachi HT7800 TEM system at 100 kV. Elemental content was determined by iCAP RQ inductively coupled plasma mass spectrometry (ICP-MS) (Thermo, Waltham, MA, USA). For ICP-MS measurements in single-particle mode (spICP-MS), experiments were conducted on a NexION 350X ICP-MS instrument (PerkinElmer, Waltham, MA, USA), which was equipped with Syngistix Nano application software.
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5

PEI/EDTA-Zn2+ Solutions Preparation and Characterization

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A batch of PEI/EDTA-Zn2+ solutions was prepared by mixing 0.4 g of EDTA, 0.8 g of PEI solution (50 wt% in water) and 0.4 g of Zn (NO3)2·6H2O and diluted to 200 mL with distilled water. The pH values of these solutions were, respectively, tailored as 2, 4, 6, 8, 10 and 11 by adding a suitable amount of HNO3 and NH3·H2O. After stirring for 24 h, these solutions concentrated to 50 mL in volume by ultrafiltration process. Subsequently, the concentrated solutions were diluted to 10,000 times its original weight with 1 wt% HNO3, while the Zn2+ ions concentration in the diluted solution was lower than 176 ppb (by weight). The diluted solutions were then centrifuged at 6000 rpm for 10 min and the solutions sampled in the upper layer were analyzed for the Zn2+ ions concentration with inductively coupled plasma mass spectrometry (ICP-MS, iCAP RQ, Thermo Fisher Scientific Ltd., Germany). For adsorption analysis of Zn2+ ions with PEI polymer, the PEI-Zn2+ solutions were firstly prepared by mixing 0.8 g of PEI solution and 0.4 g of Zn (NO3)2·6H2O. Likewise, the subsequent processes of sample preparation and characterization were described as the above.
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6

Catalyst Composition Analysis by ICP-MS

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The compositions of the catalysts, based on atomic
percentage and weight percentage, were determined by inductively coupled
plasma–mass spectrometry (ICP-MS) (Thermo Fisher iCAP RQ).
The digestion of the samples was performed by adding a mixture of
acids (1:1:3 H2SO4:HNO3:HCl) into
a known amount of the catalyst and heating to 180 °C for 30 min,
using the digestion Microwave Multiwave GO from Anton Paar. The solution
was then filtered to remove any remaining carbon residues and then
diluted 100 times in 3% HCl. The electrolyte was diluted 3.33 times
in 3% HCl.
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7

Sodium Content Determination in Tissue

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For each sample, a total of 0.05 g of dry tissues power were weighed and immersed in 4 mL concentrated nitric acid with 2 mL 30% H2O2 overnight, and then were decocted with temperature gradient (60 °C for 1 h, 120 °C for 1 h, 160 °C for 1 h, 190 °C until the solution was clarified) using a graphite digestion instrument (DigiBlock ED54, Beijing, China). The content of extracted Na+ was measured by inductively coupled plasma-mass spectrometry (ICP-MS) (iCAP RQ, Thermo Fisher Scientific, 168 Third Avenue, Waltham, MA, USA) after acid catching, constant volume and filtration with three biological replicates per sample.
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8

Honey Mineral Quantification via ICP-MS

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The mineral elements of AFH was estimated using inductively coupled plasma mass spectrometry (ICP-MS) based on the methods defined in Chinese National Food Safety Standards (GB 5009. 268–2016) [62 ]. Briefly, 0.5000 g of honey was dissolved in nitric acid (65%, 5 mL), and were allowed to digest under room temperature overnight. Then, the mixtures were dissolved in hydrogen peroxide (30%, 2 mL) before being digested at 140 °C for 2 h. The digestion was made up to 10 mL with nitric acid (2%) after being cooled. The solutions were centrifugated at 10,000 r/min for 10 min and the supernatant was kept to analysis.
Metal determination was determined using an inductively coupled plasma mass spectrometer (ICAPRQ, Thermo Fisher Scientific, MA, USA). The instrument was carried out with following conditions: RF power, 1500 W, plasma gas flow rate, 15 L/min, carrier gas flow rate, 0.8 L/min, auxiliary gas flow, 0.4 L/min, helium flow, 5.0 L/min, spray chamber temperature, 2 °C, and acquisition mode, spectrum. The content of each metal in honey was calculated with a corresponding standard curve, and expressed as mg/kg honey.
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9

In Vivo Imaging and Biodistribution of Tumor-Targeting Nanoparticles

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The intracranial tumor‐bearing rats were injected with 1 mL of PPA@DiR/MnO or iRPPA@DiR/MnO via the tail vein at a dose of 1 mg DiR kg−1 body weight. The fluorescent images were obtained using an in vivo imaging system (Carestream IS 4000, USA) before injection and at 2, 4, 6, 12, 24, 48, and 72 h after injection. At 72 h post‐injection, rats were sacrificed to obtain the major organs (heart, lungs, liver, spleen, and kidneys) and tumors for ex vivo imaging. To detect the dynamic changes in MRI signal intensity, an in vivo MRI study was performed on a clinical 3.0 T MR system (Achieva; Philips Medical Systems). After injection of PPA@TMZ/MnO or iRPPA@TMZ/MnO via the tail vein at a dose of 2 mg Mn kg−1 body weight, the tumor‐bearing rats were imaged at various time intervals by using the MRI unit with the same parameters as used in a previous study.[33] The distribution and accumulation of Mn deposits in major organs and tumors were further detected by ICP‐MS. Briefly, before and 6, 12, and 24 h after injection of PPA@TMZ/MnO or iRPPA@TMZ/MnO, the major organs (heart, lungs, liver, spleen, and kidneys) and tumors were harvested, dissolved in a mixture of 30% hydrogen peroxide solution and nitric acid, and digested using a microwave system. The Mn content was then measured by ICP‐MS (iCAP RQ, Thermo Fisher Scientific, USA).
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10

ICP-MS Analysis of Elemental Composition

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ICP-MS by an iCAP RQ (Thermo Scientific) was used to determine
the elemental composition of the samples. Prior to ICP analysis, the
samples were dissolved in a mixture of 6 mL of HCl, 2 mL of H2SO4, and 2 mL of HNO3 and subsequently
digested in a microwave (Multiwave GO, Anton Paar) at 180 °C
for 30 min. For the ICP measurement, the samples were further diluted
with ultrapure water (18.2 MΩ·cm).
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