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64 protocols using icap qc

1

Comprehensive Elemental and Organic Analysis of Snow and Ice

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The concentrations of dissolved inorganic major, minor, and trace elements in snow and ice samples were analyzed by inductively coupled plasma mass spectrometry (ICP‐MS; Thermo Fisher iCAPQc) following methods described in McCutcheon et al. (2021 (link)). The precision of the analyses varied between 2% and 5%. Inorganic anions were analyzed by ion chromatography (IC) using conductivity detection (ICS 3000, Dionex). DOC was analyzed by liquid chromatography‐organic carbon detector (LC‐OCD) where organic carbon was quantified by infrared detection of released CO2 after UV photo‐oxidation (185 nm) in a Gräntzel thin‐film reactor following Regenspurg et al. (2018 (link)).
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2

Elemental Analysis of Samples by ICP-MS

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About 0.5 g of each sample was transferred into a microwave vessel and the exact mass was measured. All samples were decomposed at 180ºC in a mixture of nitric acid (65%) and hydrogen peroxide (30%) at a 4:1 ratio (v/v). Digestion was carried out under the following microwave program: 10 min warm-up to 180ºC and heating for additional 20 min. After cooling to room temperature, decomposed samples were transferred into volumetric flasks and diluted with ultrapure water to 25 mL. All elements were quantified by inductively coupled plasma-mass spectrometry, ICP-MS (iCAP Qc, Thermo Scientific, UK) in the optimized mode of action and by applying the internal standardization. Good linearity for each element (R > 0.99) was obtained in the range from 1 to 250 µg/L. The accuracy of the ICP-MS was controlled by SRM (Seronorm™ Trace Elements Whole Blood Level-1). The obtained recovery values for elements in the SRM was in the range from 94.2 to 105%.
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3

Comprehensive Soil Geochemical Analysis

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Soil pH was determined in the mixture of fresh soils and deionized water (1:2.5, w/w) using a pH monitor (Mettler Toledo, Switzerland, FE-28-Standard). The contents of total carbon (TC) and inorganic carbon (IC) in the soils were measured using a carbon analyzer (Shimadzu Corp., Kyoto, Japan, SSM-5000 A). The total organic carbon (TOC) content in soil samples was calculated by subtracting the IC content from the TC content. Total nitrogen (TN) content in the soils was tested using an elemental analyzer (Elementar corp., Germany, vario EL cube). The soil SWC was determined by freeze-drying approximately 5 g of the fresh soils for 48 h at –40°C. Following soil extraction using 2 mol⋅L-1 KCl solution [the ratio of soil to KCl solution, 1:10 (w/w)], the contents of NO3+-N and NH4+-N were measured using a continuous flow analyzer (Skalar, Holland, San ++). Elements, including Cr, Co, Ni, Cu, Zn, As, Se, Cd, Sn, Sb, Hg, and Pb, were analyzed using an inductively coupled plasma mass spectrometry (ICP-MS) (Thermo Fisher Scientific, iCAP Qc).
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4

Placental Selenium Content Analysis

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Analysis of Se content in the placenta was performed as described previously [78 (link)]. Each placental sample was precisely weighed on an analytical balance and transferred to a microwave cuvette. Four milliliters of nitric acid (65%) and 1 mL of hydrogen peroxide (30%) were added to each microwave cuvette. Microwave digestion was performed at 180 °C (the temperature was gradually increased to 180 °C for 20 min and remained at the same value for an additional 10 min). Next, the cooled, digested samples were diluted with Milli-Q water into 25 mL normal vessels. Se was quantified using inductively coupled plasma mass spectrometry (ICP-MS, iCAP Qc, Thermo Scientific, UK) in the optimized mode of action and by applying internal standardization. Good linearity (R > 0.999) was obtained in the range from 1 to 300 µg/L. The accuracy of ICP-MS was controlled by SRM (Seronorm™ Trace Elements Whole Blood Level-1, Sero, Billingstad, Norway) and the recorded recovery values were in the range of 96.6 to 105%.
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5

Trace Element Concentration Analysis

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All samples were processed,
prepared, and analyzed in the SWAMP lab. Sample bottles were opened
only when inside class-100 laminar flow clean air cabinets (NuAire
Laboratory Equipment). Samples were analyzed inside a class-1000 clean
room. Dissolved TE concentrations were measured using quadrupole ICP–MS
with high-purity He collision gas (iCAP Qc, Thermo Fisher Scientific).
To ensure accurate results and the absence of matrix effects, standard
reference materials for TEs in surface waters (SRMs; NIST 1640a and
SPS-SW2) were respectively measured at dilution factors of 10-fold
and 100-fold and 100-fold and 500-fold after every 12–15 samples
(recoveries deemed acceptable when between 80 and 120%). Detection
limits were determined as the mean concentration + three times the
standard deviation corresponding to the number of counts per second
in five blanks of 2% HNO3. Instrument running and quality
control parameters are provided in the Supporting Information and in previous publications7 (link),30 (link) (Tables S3–S6). Samples for quasi-total
TE concentrations (i.e., acid-extractable) were first solubilized
in pure double-distilled nitric acid using high-pressure and high-temperature
microwave-assisted digestion (UltraCLAVE, ATS Scientific). Soil and
water SRMs were also digested and analyzed to ensure adequate recovery
(NIST 1640a, 2711; SPS-SW2).
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6

Quantitative Elemental Analysis of Urine

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The elementomics quantitative analysis was performed with an iCAP Qc inductively coupled plasma mass spectrometry (ICP-MS) instrument (Thermo Scientific) according to our previous report (Silver et al. 2018 (link)). Briefly, 60μL of urine and 150μL nitric acid were mixed for 3 h, and the samples were mixed with water to the volume of 1.8mL . After centrifugation, the supernatant was subjected to ICP-MS analysis. The limit of detection was defined as three times of the standard deviation (SD) of the obtained concentrations in the blank with 10 replicates. Quality control and blank samples were analyzed with study samples. Because of the amount of sample available, a total of 963 urine samples in the first trimester were analyzed for the inorganic exposome profiling.
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7

Highly Sensitive Bone-Implant-Interface Analysis

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Highly sensitive analysis of the bone-implant-interface was performed using a laser ablation system (LSX 213, CETAC Technologies, Omaha, NE) coupled to an inductively coupled plasma quadrupole mass spectrometer (iCAP Qc, Thermo Fisher Scientific, Bremen, Germany) as described by Blaske et al. [19 (link)] to address possible migration of metal components from the stem surface into the surrounding tissue. A collision/reaction cell was used for quadrupole-based MS detection to discriminate polyatomic ions (91Zr16O+), resulting from the blasting process of the titanium stem, which could possibly interfere with 107Ag+, by their kinetic energy.
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8

Microwave Digestion and ICP-MS Analysis

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A microwave digestion system (MARS6, CEM, USA) was used for sample preparation. The concentrations of Pb, Cd, As, Hg, and Cu were identified using an Inductively-Coupled Plasma Mass Spectrometer (ICP-MS, ICAP Qc, Thermo Fisher Scientific, Waltham, MA). Ultra-high-quality water (18.2 MΩ/cm) was produced by a Milli-Q advantage, Merck Millipore (Shanghai, China).
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9

Quantitative Analysis of Elemental Composition in Whole Flour

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Whole flour (0.2 g) samples were introduced into digestion tubes for digestion with 6 mL of nitric acid (HNO3) in a microwave digester. The digested solutions were filtered through a 0.45 μm water-based microporous membranes after dilution to a constant volume of 50 mL with deionised water. Subsequently, the concentrations of different metal elements including, Ca, Mn, Fe, Cu, Zn, Se, As, Cd, and Pb, were determined using inductively coupled plasma-atomic emission spectrometry (ICP-MS, Thermo Fisher, iCAP Qc). The standard curves for the different metal elements are shown in Fig. S1, and the correlation linear valuer [2 (link)]. was between 0.9977 and 0.9999. The recovery rates of all the elements ranged between 80 and 120%.
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10

Bamboo-Based Composite Material Characterization

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To obtain the surface morphologies and the content of zinc, the composites were investigated by using transmission electron microscopy (TEM, Hitachi, H-7650, Tokyo, Japan) and scanning electron microscopy (SEM, Hitachi, S-4800) combined with an energy dispersive X- analysis system. The chemical compositions of the bamboo were tested by the Fourier transform infrared spectroscopy (FTIR, Nicolet 6700, Waltham, MA, USA). A X-ray diffraction (XRD) instrument (Bruker, D8 Advance, Karlsruhe, Germany) was used to carry out the XRD measurements by utilizing Cu Kα1 radiation in the 2θ range of 5°–60°. The thermal performances of the samples were investigated by a TG analyzer (Q600, TA Instruments, New Castle, DE, USA) from 25 °C to 1000 °C under a nitrogen atmosphere with a heating rate of 10 °C·min−1. The release of zinc ions was tested by inductively-coupled plasma mass spectrometry (ICP-Ms, Thermo, ICAP-QC, Waltham, MA, USA).
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