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482 protocols using «x series 2»

1

Removal of Pb(II) from Mine Wastewater using REEs/C

2025
To evaluate the removal capacity of various REEs/C, we designed an experiment for removing Pb(II) utilising three tested REEs/Cs. Briefly, REEs/C (0.05 g) and 15 mg·L− 1 Pb(NO3)2 solution (50 ml) were put into a 150 ml transparent glass conical flask together. Then, it was shaken at 30°C and 250 rpm for 90 min to ensure sufficient reaction between REEs/Cs and lead nitrate solution. Ultimately, a pure Pb(NO3)2 solution was obtained by filtration through a 0.22 μm filter for analysis using Atomic Absorption Spectrometer (AAS, VARIAN AA240, USA). The concentration of REEs in solution was analysed by Inductively Coupled Plasma Mass Spectrometry (ICP-MS, X-Series 2, Thermo Scientific, Massachusetts, USA). Three replicates were set up for all treatments.
The removal experiment of heavy metal in mine wastewater was designed to test the potential of REEs/C for practical applications. Briefly, REEs/C (0.1 g) was placed in a 150 ml clear glass conical flask along with actual wastewater (50 ml) from a mine in Fujian Province. Then, it was shaken at 30 °C and 250 rpm to ensure sufficient reaction between REEs/Cs and lead nitrate solution. Finally, 1 mL was sampled at 0.5, 1, 4, 8, 12, 24, 48, and 72 h. The solution to be measured was obtained by filtration through a 0.22 μm filter, and was used to detect the concentration of each heavy metal ion using ICP-MS. Three replicates were set up for all treatments.
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2

Fabrication of Zinc-Bioceramic Microneedles

2025
The microneedles were fabricated via a polydimethylsiloxane (PDMS) mold with a microneedle array dimension of 20 × 20. Briefly, 2 g of sodium hyaluronate was dissolved in 50 ml of deionized water at 37 °C. Subsequently, 0.5 g of HSA (hardystonite) bioceramic was added to the solution, followed by continuous stirring for 24 h. Afterward, 1 ml of the solution was dispensed onto the PDMS mold and subjected to vacuum drying at 37 °C for 2 h. Finally, the mold underwent demolding in an oven at 37 °C for 72 h to yield ZnCS-loaded MNs (ZnCS/MN). Pure sodium hyaluronate microneedles (Blank) and CS-loaded microneedles (CS/MN) were also prepared as control groups via the same protocol with equal amounts of the corresponding ingredients. The ion (Zn2+ and SiO32−) release concentrations were measured via inductively coupled plasma–atomic emission spectrometry (ICP–AES; Thermo Fisher X Series 2, USA) from day 1 to day 5.
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3

Uranium Quantification in Plants via ICP-MS

2025
Samples consisting of 0.3 g dry weight of shoots or roots (prepared as a homogeneous mixture from pieces of 30 treated plants) were subjected to digestion using 6 mL of nitric acid (HNO3), 0.5 mL of hydrofluoric acid (HF), and 1 mL of hydrogen peroxide (H2O2) at temperatures ranging from 120 °C to 200 °C for a duration of 1 h. The uranium concentrations were then quantified using an inductively coupled plasma mass spectrometer (ICP-MS, model X-Series II by Thermo Fisher Scientific, (Waltham, MA, USA)). By interpolating the elemental signal values obtained from the samples onto a calibration curve, the total uranium concentration within each sample was determined.
The plant concentration factor (PCF) was calculated on dry weight basis as per [36 ,56 (link)]
PCF=Cplant / Csoil
where Cplant and Csoil represent the metal concentration in plant roots and soils on dry weight basis, respectively.
The plant transfer factor (TF) was also calculated on dry weight basis [56 (link)].
TF=Cshoot / Croot
where Cshoot and Croot represent the heavy metal concentration in shoots and roots of plants on dry weight basis, respectively.
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4

Lung Nanoparticle Retention Kinetics

2025
After sacrifice, the right lung lobes (from 6 animals per group) were cut into smaller pieces and subjected to lyophilization and subsequent low-temperature ashing. The remaining ash was put into 25 ml water (Milli-Q) and shaken until homogeneous. After a further 30-min period the particle suspension was filtrated using Nucleopore™ filters with pore size 0.2 µm (Whatman Co., USA). This pore size is able to separate almost completely the particulate matter from ionic titanium. Afterwards, the filter was rinsed with 25 ml additional water. The test items were analyzed via ion-coupled plasma mass spectrometry (ICP-MS; X Series 2, ThermoFisherScientific™). Recoveries: Plasma ashing—Ionic Ti: 103–105%; Filtration—Ionic Ti: 96%; Chemical analysis—QC standards: 101%; NBS SRM 349: 102%—LoQ: 10 ppb.
In addition, particle retention was determined in exemplary organs, such as the liver and brain.
The retention half-times in lungs were calculated assuming a first order kinetics (m = m0 x e−kt). An exponential curve fit was processed based on the individual retention data at day 3, 45, 94 post-exposure (3 time-points; 6 animals each) in order to calculate the clearance coefficient and the half-time: k = ln2/t1/2 (Statistica™ software).
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5

Toenail Trace Element Analysis Protocol

2025
After the interview, toenail samples (both feet) from the 55 participants were collected with nail clippers made of stainless steel within 2 weeks of recruitment, placed in a clean plastic bag and stored at room temperature. Moreover, anthropometric data and other information were obtained following the study protocol, which was approved by the recruiting centres.
First, toenail (50–100 mg) samples were washed twice with 2 mL of a 5% (weight/volume) Triton water solution; secondly, they were washed twice using 2 mL of Milli-Q water; thirdly, they were washed twice using 2 mL of acetone; and fourthly, an additional ultrasound treatment (5 min) was conducted. After that, toenails were air-dried and digested with 800 µL of a (4:1) mixture of HNO3 and H2O2 of Ultra Trace Metals grade quality, in a Teflon reactor for microwave-assisted attack. Mineralisation was performed at 400 W, starting from room temperature, ramped up to 160 °C for 15 min, and held for 20 min at this temperature. Finally, the extracts were filtered through a 0.45 µm Polytetrafluoroethylene (PTFE) membrane filter before analysis.
The elemental content of 16 metal(loid)s (Al, As, Cd, Co, Cr, Cu, Fe, Mn, Mo, Ni, Pb, Se, Tl, U, V, and Zn) in toenails was determined by an inductively coupled plasma mass (ICP-MS) system, using an XSeries 2 (Thermo Fisher Scientific Inc., Waltham, MA, USA) spectrometer at the Environmental Bioanalytical Chemistry Unit of Huelva University (Huelva, Spain). Analyses were performed blindly from the case-control status. The measured concentration was adjusted by the equipment, taking into account the dilution factor and sample weight, according to the following formula: Real μg·kg1=Equipment μg·kg1 dilution factor (g)sample weight (g)
The limit of detection for each measured element was obtained from the calibration curve [41 ].
To control the quality of analysis, the following operations were conducted: (a) 100 mg of human hair was used as reference material (NSC DC73347a) with the purpose of correcting the instrumental variability in each sample batch, with a mean accuracy of 90% maintained along the time ±5%; (b) the ICP-MS response was monitored over time by a measurement of metal(loid)s concentrations at a point on the calibration curve (2 ng mL−1) every 20 samples analysed, ensuring an adequate evaluation of the instrument’s response; (c) an instrumental drift correction was performed with the addition of 100 ng mL−1 rhodium, as an internal standard, to all of the samples and calibrants, of which those whose response differed ± 10% with respect to the internal standard were measured again; (d) an analysis was conducted every 5 samples of reagents blanks containing 5% (v/v) HNO3 (Suprapur quality), 1% (v/v) HCl, and Rh 100 ng mL−1 in Milli-Q water; (e) an analysis was conducted of duplicate samples every 2.5 h of the sequence; (f) a spiked sample analysis was conducted by spiking the reference materials with the analytes under study (50 ng mL−1). Finally, potential interferences from 98Mo, 205Tl, and 238U, regularly existing in nails, were removed by operating the ICP-MS system in helium collision mode (He flow: 4 mL min−1); the operative conditions of ICP-ORS-MS are shown in Table 1.
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Top 5 protocols citing «x series 2»

1

Elemental Imaging of Human Liver Tissue

A quadrupole-based inductively coupled plasma mass spectrometer (ICP-MS, XSeries 2, Thermo Scientific, Bremen, Germany) coupled to a laser ablation system (NWR 213, New Wave Research, Fremont, CA, USA) was used to study elemental distributions in tissue sections of human livers (30 µm thickness). Laser ablation of biological tissue was performed using a focused Nd:YAG laser beam in the scanning mode (wavelength 213 nm, repetition frequency 20 Hz, laser spot diameter 60 µm, scanning speed 60 µm s-1, laser fluency 0.24 J cm−2). The ablated material was transported by argon gas (as carrier gas) into the inductively coupled plasma (ICP). The ions formed in the atmospheric pressure ICP were extracted in the ultrahigh vacuum mass spectrometer via a differential pumped interface, separated in the quadrupole mass analyzer according to their mass-to-charge ratios and detected by an ion detector. No reference standard materials for quantification of metals in human liver were available. Therefore, SRM NIST 1577b (bovine liver) was used as standard reference material. The trace metal concentrations in the samples were determined by single point calibration using this SRM. Moreover, the selection of internal standard element is the important part for LA-ICP-MS analyzing. The appropriate internal standard element was chosen to correct for plasma instabilities and sample-to-sample variations in the ion signal intensity. In this work, sulphur was used as an internal standard element for all the analyses because sulphur in human livers present rather a homogeneous distribution and provide constant concentration (see below). The human liver tissue and the NIST standard reference material deposited on glass slide were mounted in the laser ablation chamber to perform LA-ICP-MS imaging of sample and standard reference material under identical experimental conditions. Mass spectrometric measurements by LA-ICP-MS for imaging of liver tissue were performed by line scanning ablation (line by line) with a focused laser beam under the optimized experimental parameters given in Table 2. The experimental parameters of LA-ICP-MS were optimized with respect to the maximum ion intensity of 63Cu+ using a SRM 1577b bovine liver standard. To validate the metal ion images, two isotopes of the same element were analyzed, whenever possible. From the continuous list of raw pixel values elemental images were reconstructed using the IMAGENA LA-ICP-MS Image Generation software created at Forschungszentrum Juelich [20] . Trace metal concentrations were calculated from ion intensities averaged throughout freely drawn regions of interest (ROIs) within ion intensity images using PMOD version 3.0 (details see www.pmod.com).
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2

Magnesium Isotope Analysis of Meteorites

Whole rock fragments of D’Orbigny, Sah99555 and NWA1670 weighing around 1 g were mildly crushed with an agate mortar and pestle, rinsed in acetone and distilled water and sieved. Whole rock samples of approximately 20 mg were taken from the 250–500 µm size fraction of D’Orbigny and Sah99555. Feldspar separates were generated from the remaining size fraction of these two meteorites with a Frantz isodynamic magnetic separator whereas olivine and pyroxene separates were handpicked from the crushed bulk sample. Due to the cryptocrystalline nature of the NWA1670 groundmass, only olivine and cryptocrystalline ground-mass separates of a few mg each were handpicked. Samples were digested using HF–HNO3 acid mixtures and, after complete dissolution, Al/Mg ratios were determined on an aliquot of the digested sample to 2% accuracy using a ThermoFisher X-Series II inductively coupled plasma source mass spectrometer (ICPMS).
Magnesium was purified by ion-exchange chromatography and its isotopic composition analyzed using a ThermoFisher Neptune Plus multiple collector ICPMS (MC-ICPMS) equipped with a Sampler Jet and Skimmer X-cone and an Apex sample introduction system following protocols outlined in Bizzarro et al. (2011) . The Mg isotope composition was measured in high resolution mode using a 50 μm entrance slit (MM > 5000). At an uptake rate of ~50 μL/min, the sensitivity of the instrument was ~200 V/ppm. Depending on sample size signal intensities were typically 100 V or 25 V on mass 24Mg (see Table 1). Faradays cups that received signals larger than 50 V were connected to an amplifier with a 1010 Ω feedback resistor, whereas Faradays cups collecting smaller signals were connected to an amplifier with a 1011 Ω feedback resistor. Single analyses comprised 1667 s of data acquisition and each sample was bracketed by standard analyses and analyzed ten times when permissible. Mg isotope data are reported in the μ-notation as relative deviations from the DTs-2b standard (µ25MgDSM-3 = −122 ± 17 ppm (2 sd); Bizzarro et al., 2011 ) according to the following formula: μ25Mg=[(25MG/24Mg)sample(25Mg/24Mg)DTS2b1]×106.
The mass-independent component in 26Mg (µ26Mg*) is reported in the same fashion, but represents deviations from the internally normalized 26Mg/24Mg of the sample from the reference standard, normalized to 25Mg/24Mg = 0.126896 using the exponential mass fractionation law. We used the exponential law (β = 0.511) to correct for instrumental mass bias and potential natural mass fractionation experienced by the samples. Two lines of evidence indicate that this approach yields accurate 26Mg* values. First, the rock samples analyzed here are rapidly cooled magmatic lavas and, under such conditions, equilibrium mass fractionation is believed to be negligible (Teng et al., 2007 ). Second, instrumental mass fractionation under typical analytical conditions in our laboratory is driven by kinetic processes rather than equilibrium (i.e., Bizzarro et al., 2011 ). As such, variable instrument-related mass fractionation in samples relative to the standard can be accurately corrected for using our approach. We note that, similar to earlier studies (Spivak-Birndorf et al., 2009 ; Schiller et al., 2010 ), stable isotope variability exists between individual mineral fractions, typically for samples containing little Mg. We infer that this reflects analytical artifacts in the stable isotope data during analysis by MC-ICPMS induced by the presence of residual organics accumulated in the purification process rather than true isotope variability. Thus, we caution that the reported internal uncertainties for 25Mg do not reflect the true reproducibility of the data, which may be significantly larger for small samples.
All Mg data reduction was conducted off-line using Iolite (Paton et al., 2011 ) and changes in mass bias with time were interpolated using a smoothed cubic spline. For each analysis, the mean and standard error of the measured ratios were calculated using a 3 sd threshold to reject outliers. Individual analyses of a sample were combined to produce a weighted average by the propagated uncertainties of individual analyses and reported final uncertainties are the 2 se of the mean. 26Al–26Mg isochrons were calculated based on 27Al/24Mg and Mg isotope data reported in Table 1 using Isoplot applying an external reproducibility of the μ26Mg* data of 2.5 ppm for samples analysed systematically ten times at signal intensities of ~80 V for 24Mg (Bizzarro et al., 2011 ). Samples measured at intensities of ~25 V for 24Mg yielded a larger external reproducibility of 5 ppm that is predicted by counting statistics for approximately four times lower signals.
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3

Laser Ablation-ICP-MS Imaging of Trace Metals in Tissues

In the experimental setup that we used for our measurements, a quadrupole-based inductively coupled plasma mass spectrometer (XSeries 2, Thermo Scientific, Bremen, Germany) was coupled to a laser ablation system (NWR 213; New Wave Research, Fremont, CA, USA). For metal imaging in murine and human liver tissue, 30 μm thick tissue cryo-sections were prepared and laser ablation of biological tissue was performed essentially under conditions that were described before 14 (link). The ablated material was transported by argon gas into the inductively coupled plasma and the formed ions were extracted in the ultrahigh vacuum mass spectrometer via a differential pumped interface, separated in the quadrupole mass analyser according to their mass-to-charge ratios, and detected by an ion detector (Fig. S1). All trace metal concentrations were calculated from ion intensities averaged throughout freely drawn regions of interest and representative images were generated from the continuous list of raw pixel values using modified in-house LA-ICP-MS Image Generation software that is based on the IMAGENA software originally created at the Research Centre Jülich 22 . For quantification purposes, matrix-matched laboratory standards were prepared by dosing each analysed element to the pieces of homogenized tissue that were essentially prepared as described 15 . As a surrogate of slice thickness, the metal intensities were normalized to the average 13C ion intensity of respective samples in each measurement as suggested elsewhere 23 (link).
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4

Laser Ablation ICP-MS for Quantitative Imaging

A commercial laser ablation (LA) system (New Wave UP 266, Fremont, CA, USA) operated with a frequencyquadrupled Nd:YAG laser (wavelength of 266 nm, repetition frequency of 20 Hz, spot diameter of 110 μm, distance between lines of 50 μm, scan speed of 30 μm/s) was coupled to a quadrupole ICPMS (XSeries2, Thermo Fisher Scientific, Germany). The experimental parameters of LA-ICPMS were optimized with respect to the maximum ion intensity of 63Cu+ using a laboratory standard. Maximum ion intensity was observed at an rf ICP power of 1500W and a carrier gas flow rate of 1.2 L min−1 for the transport of ablated material to the ICPMS. Twenty-seven different mass-to-charge ratios (m/z), corresponding to selected isotopes of 16 elements, in the range from m/z 6 to m/z 300 were preset and determined within a cycle time of 2.7 s that constitute one pixel. Thus, the resolution was 30 μm/s × 2.7 s = 83 μm in ×- and 110 μm + 50 μm = 160 μm in y-direction. As the entire thickness (<100 μm) of a tissue section is ablated, the data represent an average across the thickness of the tissue section. Thus, the spatial precision of the distribution of analytes is maximized, and challenges associated with the vertical transport of solutes during drying, by surface contaminations or by analyte fractionation effects during ablation, are minimized. The spatial resolution in x-direction is given by the product of the x-speed of the piezo-driven xyz-stage and the cycle time; the spatial resolution in y-direction by the preset distance between the centers of lines. The spot size of the laser does not directly influence the spatial resolution. We obtained best results with xand y-step width smaller than the laser spot diameter in the sense of oversampling, leaving about 5 μm wide bars of residual tissue between ablated lines.
Matrix matched standards were prepared from homogenates of mouse brains spiked with 1/9 volume of the dilutions 0, 0.2, 0.4, 0.6, 0.8, and 1 of a multielement standard solution that contained the 10-fold of the expected maximal physiological concentrations, i.e., of 30.0, 20.0, 19.8, and 0.37 μg g−1 Zn, Cu, Fe, and Mn, respectively. Every step was weight monitored, and aliquots of the spiked homogenates further characterized by ICPMS of microwave induced acidic digests. Starting with added concentration 0 (blank), homogenates were subsequently palmed off and frozen as 2 mm thick layers in a cylindric mold resulting in a stack that was chucked in the cryo-microtome with the cylinder axis almost parallel to the blade. Hundreds of 30 μm thick cryosections of these standards were obtained and placed onto glass slides.
In order to correct for the variation of slice thickness of samples and standards, the net ion intensity of 13C+ averaged over the section or the rectangle ablated from the standard stripes proportional to the content of dry organic matter was considered as a substitute of the slice thickness. Net count rates from the standard and the section were normalized to the average net 13C+ signal: CX, corr = ([13C+]Std/[13C+]Sec) × [X]/mx, with CX, corr, corrected concentration of element X; [13C+]Std, [13C+]Sec, averaged net 13C+ ion intensities of the standard and the section; [X], ion intensity of the m/z corresponding to element X within the pixel or within the region of interest; mx, slope of the calibration line for element X.
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5

Arsenic(III) Adsorption Performance of Templated Membranes

All experiments conducted to determine the As(III) adsorption performance of TeMs were carried out using batch equilibrium techniques. Feed As(III) solution (100 ppm, pH 4.0) was prepared by diluting the certified As(III) reference solution (0.1 g/L, Ecroskhim, Russia). Adsorption kinetics were studied at an As(III) concentration of 50 µg/L (pH 4.0). Disposable plastic vials (Isolab, Eschau, Germany) containing 15.0 mL of solution and 2 × 2 cm of composite adsorbate were shaken (100 rpm, IKA KS 3000 IS control, (IKA, Konigswinter, Germany) at room temperature for different times between 15 min and 10 h. Each experiment was repeated in triplicate. The concentration of As(III) in aliquots was determined by ICP–MS (Thermo Fisher Scientific, XSeries 2, Bremen, Germany). The adsorbed amount of As(III) was calculated using Equation (2) [34 (link)]: Qe=(C0Ce)×Vm
where Qe is the amount of As(III) adsorbed by the unit mass of TeMs (mg/g), C0 is the feed concentration (mg/L), Ce is the concentration of As(III) in aliquots (mg/L), V is the volume of the solution (L), and m is the amount of silver loaded on the membrane used (g). In the case where the pristine template was tested, the weight of PDMAEMA-g-TeMs and Q-PDMAEMA-g-TeMs were used in m (g).
The effect of pH on As(III) adsorption was studied in the pH range of 3 to 9. Other parameters were kept constant (initial As(III) concentration: 50 ppm; adsorbent dose: 2 × 2 cm2; contact time: 300 min). The pH of the solution was adjusted dropwise with 1.0 N HCl(aq) and 1.0 N NaOH(aq). The pH was measured using a digital pH meter, HANNA HI2020-02 (HANNA Instruments, Smithfield, UT, USA). All experiments were performed in triplicate.
The charge on the adsorbent surface depending on the pH value was studied by determining the pHzpc value in the pH range from 3.0 to 9.0 according to the method described in ref. [54 ]: 10 mL of NaCl solution (0.01 M.) was brought to the desired pH value (pHi) by adding 0.1 M. of HCl or NaOH. After that, sample with the size of 2 cm × 2 cm was added to each flask and shaken on a shaker IKA KS 3000i (IKA, Konigswinter, Germany) for 12 h at room temperature and the final pH (pHf) of the filtrate was measured using HANNA HI2020-02 pH-meter (HANNA Instruments, Smithfield, Smithfield, UT, United States of America).
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