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36 protocols using icap rq icp ms

1

Cadmium Quantification in Medicinal Herb

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Dried S. miltiorrhiza root and leaf samples (0.05 g) were digested with 10 mL of nitric acid in a polytetrafluoroethylene container into a microwave digestion apparatus. The digested samples were poured into a Teflon beaker, heated to nearly 1 mL, and adjusted the volume to 50 mL in a centrifuge tube. The iCAP™ RQ ICP-MS (Thermo Fisher, USA) was used to determine Cd content in the roots and leaves of S. miltiorrhiza. The bioaccumulation quantity (BCQ) was calculated as the product of Cd concentration in different tissues and their dry weights.
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2

Comprehensive Water Quality Analysis

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Total metals were measured
following acidification with 2% v/v nitric acid using inductively
coupled plasma mass spectroscopy (iCAP RQ ICP-MS; Thermo Fisher Scientific,
Waltham, WA). Phosphate was measured using a 4500 HACH spectrophotometer
with PhosVer3 ascorbic acid (Method 8048, HACH, Loveland, CO). Total
chlorine and total ammonia were monitored in influent water using
a 4500 HACH spectrophotometer with DPD (Method 8167, HACH) and salicylate
(Method 8155, HACH) and were confirmed to be low (<0.05 mg/L total
chlorine and <0.06 mg/L NH3-N).
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3

Quantifying Intracellular Metal Levels

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The total amounts of Mn2+, Fe, and Zn2+ were quantified from 5-ml cultures. Cells were grown overnight in LB broth and then inoculated in LBK pH 6.8, and LBK pH 8.4 media supplemented with 1 mM IPTG and appropriate concentration of ampicillin respectively. After growth to the mid-log phase at 37 °C, cells were harvested using centrifugation at 4000g for 10 minutes. Cell pellets were washed with 10 mM N-2-hydroxyethylpiperazine-N-2-ethane sulfonic acid (HEPES) pH 7.5, containing 2 mM EDTA and then washed twice with 10 mM HEPES as described in (Zeinert et al., 2018 (link)). Cell pellets were dried for 1 hour in a centrifuge evaporator. Dried cell pellets were solubilized in 400 μl of 30% (v/v) HNO3 and incubated at 95 °C for 10 min. Then samples were centrifuged at 20,000g for 5 minutes. Samples were prepared for inductively coupled plasma mass spectrometry (ICP-MS) by diluting 300 μl of supernatant of lysed cells into 2.7 ml of 2.5% (v/v) HNO3 and run on an iCAP RQ ICP-MS (Thermo Scientific). Metal concentrations are presented as intracellular levels after correction for mean cell volume determined from total protein content (Martin et al., 2015 (link)). The data obtained were presented from three repeats of the experiment.
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4

Thermo iCAP RQ ICP-MS Protocol

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A Thermo Scientific™ iCAP™ RQ ICP‐MS was used for all measurements. The sample introduction system consisted of a Peltier cooled (3°C), baffled cyclonic spray chamber, PFA nebulizer, and quartz torch with a 2.5 mm i.d. removable quartz injector. The instrument was operated using kinetic energy discrimination (KED) using pure He as the collision gas in the collision/reaction cell (CRC). To automate the sampling process, an Elemental Scientific SC‐4 DX Autosampler was used. Typical ICP‐MS operating parameters are summarized in Table 1
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5

Doxorubicin-Loaded Nanoparticle Encapsulation

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The encapsulation of DOX by HMON-Tf NPs, Fe-HMON-PEG NPs and Fe-HMON-Tf NPs was prepared by mixing the DOX (3 mg) with nanoparticles (10 mg) in PBS solution under dark conditions for 24 h. After that, the unloaded DOX was removed by centrifugation and the supernatants were reserved for the calculation of loading efficiency of drugs. Loading content=TD-FD/TN×100% Encapsulation efficiency=TD-FD/TD×100% where TD is the total weight of DOX fed, FD is the weight of nonencapsulated free DOX, and TN is the weight of nanoparticles.
To investigate the dissociation of DOX@ Fe-HMON-Tf NPs in response to pH and GSH trigger. A certain concentration of DOX@Fe-HMON-Tf NPs was dispersed into buffer solutions with different pH (7.4, 6.8, and 5.5) and different GSH concentrations (5 mM and 10 mM). At predetermined time points, undissolved nanoparticles were removed by centrifuging at 12000 rpm for 15 min and the concentration of DOX in the supernatant was detected using a fluorescence spectrophotometer. And the content of iron in the supernatant was measured by an inductively coupled plasma mass spectrometry instrument (ICP-MS, ICAPRQICPMS, Thermo Fisher, USA).
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6

Trace Metal Analysis of Protein Samples

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The ICP-MS analysis was done on a Thermo Fisher Scientific iCAP RQ ICP-MS in the Environmental and Complex Analysis Laboratory (University of California, San Diego). Protein samples were prepared at 0.5 μM of monomers (10 ml) in 2% trace metal nitric acid and analyzed directly. The analysis was conducted in kinetic energy discrimination mode monitoring 45Sc and 89Y as internal standards.
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7

Trace Element Analysis in Serum

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The serum concentrations of Fe, Cu, Mn, Zn, Se, I and Co were determined in an induced coupled plasma mass-spectrometry (iCAP™ RQ ICP-MS, Thermo Fisher Scientific, Waltham, MA, USA) as described previously with minor modifications (Liu et al., 2014 (link)). In brief, 0.1 mL of reconstituted serum samples were diluted to 2 mL with a 1: 20 (v/v) sample diluent solution [constructed from 0.01% (w/v) Triton X-100, 0.005% (w/v) L-cysteine, 0.5% (v/v) nitric acid and deionized water]. The standard solutions containing the required seven single elements were purchased from the TMRM QC standards material center (Changzhou, China), and then diluted with sample diluent solution to appropriate concentrations according to the predicted concentrations of trace elements in serum. The major ICP-MS operating parameters were set as follows: Analyzer Pressure Readback, 1E-06 mbar; Spray Chamber Temperature, 2°C; Cool Flow, 14 L/min; Auxilliary Flow, 0.79 L/min; Nebulizer Flow, 1.06 L/min; Plasma Power, 1550 W; Q Cell gas, He 4.0 mL/min; injection method, automatic injection.
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8

Elemental Analysis by ICP-MS

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The ICP-MS analysis was done on a Thermo Scientific iCAP RQ ICP-MS in the Environmental and Complex Analysis Laboratory at UC San Diego. Samples were washed twice to remove unreacted reagents and then digested overnight in aqua regia before analysis.
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9

Characterization of Organic Compounds

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Melting points were determined on a RDCSY-I capillary apparatus and were uncorrected. Allmaterials used were commercially available and used as supplied. HG/T2354-92 silica gel 60 F254 sheets were used for analytical thin-layer chromatography (TLC). Column chromatography was performed on silica gel (300–400 mesh). 1H NMR spectra were recorded on a Bruker AV-300 spectrometer. Chemical shifts (δ) were given in parts per million (ppm) relative to the solvent peak. J values are in Hz. Chemical shifts are expressed in ppm downfield from internal standard TMS. Mass spectra (MS) were measured using a Thermo Scientific iCAP RQ ICP-MS. All the reagents and solvents were reagent grade and were used without further purification unless otherwise specified.
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10

Trace Metal Analysis in Water Samples

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For lead concentration determination, EPA Method 200.8 Determination of Trace Elements in Waters and Wastes by Inductively Coupled Plasma–Mass Spectrometry (ICP-MS) was used [33 ]. The limit of detection (LOD) for this method was 1 ppb. Water samples collected by EHS were sent to Pace Analytical Services, LLC (Oldsmar, FL, USA, and Mount Juliet, TN, USA). Samples collected by the consulting group were sent to ©Eurofins Scientific (Savannah, GA, USA). Samples were analyzed on a Thermo Scientific™ iCAP™ RQ ICP-MS (Bremen, Germany) in batches as they were collected. To ensure the integrity of each analysis, the quality control measures of EPA method 200.8 were used, which included the assessment of a method blank (water), a laboratory control sample, and two matrix spikes alongside their matrix spike duplicates. SRM 3128 (High Purity Standards, North Charleston, SC, USA) was used as a certified reference material for lead measurements by ICP-MS. No additional analyses for other parameters, such as pH, temperature, or conductivity, were conducted.
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