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X series 2 model

Manufactured by Thermo Fisher Scientific
Sourced in France

The X Series II Model is a laboratory equipment product designed for general use in scientific research and analysis. It provides core functionality for the intended application without any additional interpretation or extrapolation.

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5 protocols using x series 2 model

1

Hair Metal Analysis Protocol

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Hair samples were collected from only healthy men and women who had not dyed, permed, or discolored their hair in the last 3 months. Hair was collected (5–10 cm) as close to the skin of the head as possible using surgical scissors. The hair samples were then cut into 50-mg slices and washed according to International Atomic Energy Agency recommendations [14 ]. Specifically, they were rinsed once in acetone, twice in double deionized water, and once more in acetone for 10 min each time [14 ]. Fifty-milligram portions of pretreated hair samples were measured and hydrolyzed for 30 min using nitric acid and hydrogen peroxide in the Mars 6 microwave digestion system (Matthews, NC, USA). The hydrolyzed homogeneous aqueous solutions were diluted and analyzed with an inductively coupled plasma mass spectrometer (Model X series II, Thermo Fisher Scientific, Waltham, MA, USA). All chemicals were of reagent grade and obtained from Sigma Aldrich (St. Louis, MO, USA).
Statistical analysis in this study, including correlation and linear regression analyses, were performed using Minitab® software (Minitab Inc., State College, PA, USA), and sex differences were analyzed using the paired t-test.
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2

Elemental Analysis using ICP-MS

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Elemental analysis was undertaken using an ICP-MS (Model X-Series II, Thermo-Fisher Scientific) operated in 'collision cell mode' (7% hydrogen in helium) to reduce polyatomic interferences. Samples were introduced from an autosampler (Cetac ASX-520) through a concentric glass venturi nebuliser (flowrate c. 0.8 mL min -1 ). Internal standards were introduced to the sample stream via a T-piece and included Rh (20 ng mL -1 ) and Ir (10 ng mL -1 ) in 2% TAG HNO3. External multi-element calibration standards (Claritas-PPT grade CLMS-2, Certiprep/Fisher) were used for calibration. Sample processing was undertaken using Plasma lab software (version 2.5.4; Thermo-Fisher Scientific) configured to employ separate calibration blocks and internal cross-calibration where required.
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3

Quantifying Elemental Composition in Plant Samples

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The quantification of elements was performed using 250 mg of dried plant powder. Mineralization was carried out using 3.5 mL nitric acid (HNO3, 65%, analytical grade, Optima) and 1 mL hydrogen peroxide, and samples were incubated in a heating block digestion system (DigiPREP, SCP Sciences, Courtaboeuf, France). A gradual heating mode was used to achieve a final temperature of 100 °C (total run of 265 min). Then, ultrapure water (18.2 MΩ/cm2, Millipore Milli-Q Integral 3 system, Molsheim, France) was added to a final volume of 25 mL, and samples were filtrated to 1 μm. Elemental concentrations were determined by ICP-AES (Radial ICAP 6500 Model, Thermo Fischer Scientific, Courtaboeuf, France) or ICP-MS (X Series II Model, Thermo Fischer Scientific, Courtaboeuf, France) for REEs. Oriental basma tobacco leaves (INCT-OBTL-5, LGC Promochem, Molsheim, France) were used as certified reference material.
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4

Heavy Metal Analysis in Road Dust

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Road dust samples were air-dried and then filtered to remove large and thick contaminants such as cigarette butts, leaves, and rocks. The samples were then manually ground by agate mortar and pestle, passed through a nylon sieve of 0.149 mm, and stored in closed polyethylene bags before chemical assay.
For the determination of Cd, Co, Cr, Cu, Mn, Ni, Pb, and Zn concentrations, 0.1000 g samples were weighed, placed into PVC digestion vessels, and digested in an automatic graphite digestion instrument (ST-60, Polytech, Beijing, China) with a mixture solution of concentrated HNO3-HF-HClO4 [18 ,19 ]. The concentrations of the target heavy metals in the dust sample were determined by inductively coupled plasma mass spectrometry (ICP-MS; X-Series II Model, Thermo Fisher Scientific, America) and inductively coupled plasma atomic emission spectrometry (ICP/AES; ICPS-7500, Shimadzu, Japan).
To determine the concentrations of As and Hg, 0.2000 g of sample was placed into a 25 mL colorimetric tube, digested in a water bath with a mixture solution of aqua regia [20 ,21 ], and analyzed by atomic fluorescence spectrometry (AFS 830, Titan, China).
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5

REE Concentration Determination in Growth Media

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Nominal concentrations of LaCl3, GdCl3, and YbCl3 at 2 µM each and at their respective EC50 were compared with measured concentrations in the minimal growth medium (for E. coli growth microplate assays) and MOPS buffer (for subcellular parameter analyses) (Table 1). REE-containing growth medium and MOPS buffer were diluted 100 times with Milli-Q water and filtered through a 0.22-µm pore size filter prior to acidification in 2% HNO3 (69%, AppliChem Panreac). Concentrations were determined in triplicate using inductively coupled plasma mass spectrometry (ICP-MS, X Series II Model, Thermo Fischer Scientific, Courtaboeuf, France). The validity of the analytical method was checked by means of standard reference material (Surface Water -Trace metals, SPS-W1, LGC Prochem standards). Since only slight differences could be observed between nominal and measured REE concentrations in both media (Table 1), throughout the present study, nominal concentrations were used for growth curve modelling and subsequent EC50 determination.
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