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55 protocols using icp ms 7700

1

Characterization and Release of Gadolinium-Labeled Nanodiamonds

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The morphology and size of the particles were characterized with TEM (JEOL JEM-1011)58 . The stability and surface charge of HPMA-coated NDs with Gd3+ complexes were tested by dispersing them in buffer solutions (50 mM citric acid buffer pH 2.0, 50 mM acetate buffer pH 4.5, 50 mM HEPES buffer pH 7.4, 50 mM TRIS buffer pH 8.5 and 1.5 M PBS buffer pH 7.4) for further experiments. Dynamic light scattering and zeta potential were recorded with a Zetasizer Nano ZS system (Malvern Instruments) at 37 °C at a concentration of 0.1 mg ml−1.
To quantitatively measure the amount of Gd3+ complexes released from the nanosensors, the particles were mixed with buffer and incubated for a certain time. Then, cleavage conditions were stopped, the particles were centrifuged and the released Gd3+ complexes in supernatant were measured with an ICP MS 7700 (Agilent Technologies) instrument in duplicates. The non-cleavable ND-HPMA-Gd3+ conjugate was used as a control and processed under the same conditions. The relative release at a given time was calculated as a ratio of the amount released to the maximum release amount. A detailed description of these release experiments can be found in the Supplementary Information. The total amount of Gd3+ conjugated to HPMA-coated NDs was measured as ∼3.2% (weight percentage to NDs) using ICP AES (Spectro Arcos SOP).
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2

Microwave-Assisted Digestion and Trace Metal Analysis

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Prior to analysis, samples were weighed (1 ml of EDTA blood) and digested in Teflon cuvettes by adding 7 ml of 65% nitric acid and 1 ml of 30% H2O2 in a microwave oven (Milestone START D, SK-10 T, Milestone Srl, Sorisole, Italy). Sample preparation was performed in three steps: heating for 15 min at 180°C, digestion for 15 min at 180°C, and cooling for 15 min. Also, blank samples containing a mixture of 65% nitric acid (7 ml) and 30% hydrogen peroxide (1 ml) were prepared and analyzed together with the samples. After cooling, samples and blanks were quantitatively transferred to normal 10 ml vessels. Graphite furnace atomic absorption spectrophotometry (AAS GTA 120 graphite tube atomizer, 200 series AA, Agilent technologies, Santa Clara, CA, USA) was used to determine the Cd concentration. The ICP-MS method (ICP-MS 7700, Agilent Technologies, Santa Clara, CA, USA) was used for the analysis of Hg, Cr, As, and Ni. An external standard technique (multielement standard solution 1 g/L in diluted nitric acid (Merck, Darmstadt, Germany)) was applied for calibration. The accuracy of both AAS and ICP-MS was validated with standard reference material (SRM) whole blood Level 2 (Seronorm TM, Sero, Billingstad, Norway). For SRM preparation and analysis, the same procedure was applied as for the EDTA-blood samples.
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3

Phytoremediation of Copper-Contaminated Soils

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In order to remove the maximum contaminants, all plants were coppiced at the end of the growth season. To evaluate the yield, the above-ground biomass (shoots and leaves) of all plants was weighed in the field, using an electronic scale (Xiangshan Inc. model ACS- JC21D). Portions of the plants were oven-dried at 80 °C (to a constant mass) before being reweighed, to determine the average dry biomass. The below-ground biomass of all plants was the average root system estimated by the above-ground parts.
Dry plant tissues from each sample were ground with a stainless-steel grinder until all particles passed through a 0.149 mm nylon sieve, to determine the Cu concentration. Approximately 0.5 g of these samples were digested with a mixture of concentrated HNO3 (10 mL), 30% H2O2 (1 mL), and concentrated HCl (2 mL) in Teflon tubes. These digested solutions had a constant volume of 25 mL with deionized water, and 10 mL of the suspensions were filtered through a nylon membrane (Magna-0.45 mm). The Cu concentration of these digested solutions were analyzed, using ICP-MS (Agilent ICPMS 7700) [40 (link)]. The translocation factor refers to the efficiency of the plant in translocating the accumulated metal from its roots to the shoots [41 (link)].
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4

Quantifying Heavy Metal Accumulation

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The plants were harvested 60 days after transplantation. After transporting to the laboratory, each plant sample was washed with deionised water, oven-dried at 100 °C to an even weight, and separated into roots and shoots to determine the dry weight of each component for the biomass growth measurements; then, a 50–100 g dry sample was collected for chemical analysis. The dried samples were pulverised using a stainless-steel grinder and then stored at room temperature. Dry plant material (0.25 g) was digested in 8 mL of HNO3 in a microwave oven (Start 1500, MLS GmbH, Leutkirch im Allgäu, Germany) using a temperature step gradient (maximum of 210 °C). When necessary, digested solutions were diluted with 2% HNO3. The Cd and Pb concentrations in the extract solution were measured via inductively coupled plasma mass spectrometry (ICP-MS 7700, Agilent Technologies, Santa Clara, CA, USA). Blanks and a certified reference material, GBW10045 (GSB-23, rice flour), were also prepared by the digestion process for quality assurance. The recovery of the reference material was between 87% and 110%.
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5

Analyzing SMX Transformation by Cobalt-Cyanide

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Detailed information about analyses of SMX concentration and its transformation products are shown in Text S4. The PAA concentration was regularly calibrated using a colorimetric method.28 (link) The pH value of reaction solution was measured using a pH meter (PHS-3C, Leici, China). The concentration of leached cobalt ion was quantified by an inductively coupled plasma mass spectrometer (ICP-MS, Agilent ICPMS 7700, USA). The degradation of SMX in Co–CN/PAA system followed a pseudo first-order kinetic model and the observed rate constant (kobs) of SMX degradation was thus calculated viaeqn (1). where C0 and Ct refer to the concentrations of SMX at initial time and reaction time t, respectively.
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6

Soil Heavy Metal Analysis

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The soil tests were completed at the Anhui Institute of Geological Experiment. After the samples were digested by HCl–HNO3–HClO4–HF, the concentrations of Cd, Pb, and Cr were determined by inductively coupled plasma mass spectrometry (ICP-MS 7700, Agilent Technologies, Santa Clara, CA, USA); the concentrations of Hg and As were determined by atomic fluorescence spectrometry (AFS-8220, JiTian Technologies, Beijing, China) after digestion by aqua regia; the soil pH was measured using a pH meter (SG8, METTLER TOLEDO, Zurich, Switzerland). The laboratory used national standard materials and repeated sample tests for quality monitoring. The accuracy, precision, and reported percent of the various indicators were controlled at 0.10–0.12, 10–20%, and over 98%, respectively.
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7

Calcium Release from HAp/CNF Membranes

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HAp/CNF membranes of the same size were placed in centrifuge tubes containing 3 mL of culture medium. The culture medium from days 1, 3, 5, and 7 were used to measure the Ca2+ concentration using inductively coupled plasma mass spectrometry (ICP-MS) (Agilent ICPMS 7700).
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8

Elemental and Gadolinium Analysis

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The elemental analysis was performed with CHNOS Elemental Analyzer vario MICRO from Elementar Analysensysteme GmbH with sample weight approximately 2 mg. The amount of gadolinium(III) in prepared compound was determined in atmosphere of argon on ICP-MS 7700 instrument developed by Agilent Technologies.
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9

Fabrication of Dual-Loaded Nanoparticles

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The nanoparticles (HINPs) encapsulating HMME and SPIO were fabricated by using a typical double-emulsion process (w/o/w) [32 (link), 70 (link)]. Briefly, 1.4 mg HMME and 1.05 mg SPIO were added into 2 mL of PLGA (50 mg) dissolved in dichloromethane (oil phase), and 200 μL double distilled water (water phase) was added. Then, the mixture was emulsified by using an ultrasonic probe (Sonics & Materials, Inc., USA) with power of 60 W for 3 min to form the first w/o emulsion. The w/o emulsion was then poured into 10 mL 4% w/v PVA solution and emulsified for 3 min at the same power for the second w/o/w emulsion. Subsequently, 20 mL 2% v/v of isopropyl alcohol solution was added to the above emulsion to evaporate organic solvent for 6 h at room temperature. Lastly, the HINPs were collected after centrifugation at 10,000×g for 10 min. The DIR-labeled HINPs were prepared by the same method. The encapsulation efficiency (EE) and loading capacity (LC) of HMME and SPIO in HINPs were evaluated by UV–vis spectra technology (UV-3600, Shimadzu, Japan) and inductively coupled plasma mass spectrometry (ICP-MS) (Agilent ICPMS 7700), respectively. The EE and LC were calculated as described below (n = 3): EE%=HMME or SPIO encapsulated in nanoparticlesTotal HMME or SPIO added×100% LC%=HMME or SPIO encapsulated in nanoparticlesWeight of nanoparticles×100%
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10

Characterization of PQAS–AgNPs Composite

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UV-visible absorption spectroscopy (JiHong, China) with quartz cuvettes (1 cm optical path) as the containers was used to record the UV-visible absorption spectra. The morphology and the size of PQAS–AgNPs were determined by transmission electron microscopy (TEM, JEM-2011, Jeol, Japan), which was coupled with an energy dispersive spectrometer (EDS). X-ray photoelectron spectroscopy (XPS) (PHI 5600, PerkinElmer Inc.) was used to determine the valence state of the produced AgNPs. The surface charge of the AgNPs was evaluated by zeta (ζ) potential, using a Zetasizer Nano instrument (Zetasizer Nano ZS 90, Malvern, UK) at 25 °C. The concentration of synthesized composite material was calculated by silver. The silver concentration was measured by an inductively coupled plasma mass spectrometry (ICP-MS7700, Agilent, USA) after being digested with concentrated HNO3 for 2 h.
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