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Optima 8000 spectrometer

Manufactured by PerkinElmer
Sourced in United States

The Optima 8000 spectrometer is a versatile laboratory instrument designed for elemental analysis. It utilizes inductively coupled plasma optical emission spectrometry (ICP-OES) technology to precisely measure the concentration of elements in a variety of samples. The Optima 8000 is capable of analyzing a wide range of elements and offers high sensitivity, accuracy, and throughput performance.

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5 protocols using optima 8000 spectrometer

1

Shoot and Root Biomass Zinc Quantification

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Approximately 100 mg of shoot or root dry biomass was carefully weighed and mineralized in a microwave medium pressure digestor (Milestone Start D, FKV Srl, Torre Boldone, Italy) with 7 mL of 69% HNO3 and 2 mL of 30% H2O2 (ultrapure grade). Zinc concentration in the resulting solutions was determined by inductively coupled plasma optical emission spectroscopy (ICP-OES) using an Optima 8000 spectrometer (Perkin Elmer, Waltham, MA, USA), following the procedure of [83 ].
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2

Quantifying TiO2 Nanoparticle Uptake

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Cellular uptake of TiO2 NPs was determined by measuring intracellular titanium concentration using inductively coupled plasma-optical emission spectrometry (ICP-OES). Briefly, 2 × 105 cells/well were seeded in culture dishes. After adhesion, cells were exposed to TiO2 NPs (0, 25 and 100 μg/mL) under normal gravity and simulated microgravity. After 48 h, cells were washed with PBS, and collected by trypsinization. Cell count was conducted using trypan blue staining. Then cells were suspended in 100 μL PBS and stored at 4 °C until digestion. Samples were transferred to a quartz beaker, then 3 mL of ultrapure HNO3 was added and the samples were heated for 2 h at 120 °C. Afterwards, 1 mL H2O2 was added for further heating digestion, and then the samples were dried by heating at 180 °C. Next, the obtained solutions (about 200 μL) were transferred to a polypropylene vessel and diluted to 3 mL with 2% HNO3. A calibration curve was constructed using standard solutions prepared by serial dilution of a reference solution (NIM-RM3041, National Institute of Metrology, 100 mg/L) and intracellular Ti concentrations of the samples were measured with a Optima 8000 spectrometer (PerkinElmer, Waltham, MA, USA). Cellular uptake of TiO2 NPs was calculated against the cell counts (µg/105 cells).
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3

Quantification of Cerium in Biological Samples

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ICP-MS Nexion 350X with an ESI autosampler (Perkin Elmer, USA instrument, Perkin Elmer, Waltham, Massachusetts, MA, USA) was used to determine total cerium concentration in the receiver phases. A six-point standard curve obtained by the dilution of cerium standard solution for ICP-MS analysis (by Sigma Aldrich, Milan) was used for ICP-MS measurements (0.01–10 μg L−1, ion mass 140 u.m.a.). The limit of detection of cerium was 0.001 μg L−1 for ICP-MS and the precision of the measurements as repeatability (relative standard deviation (RSD) %) for the analysis was <5%.
Total cerium concentration in donor phases and in the solutions resulting from the mineralization of the skin samples were performed by (ICP-OES) using an Optima 8000 Spectrometer (PerkinElmer) equipped with an S10 Autosampler. ICP-OES analyses were conducted using a calibration curve obtained by dilution (range: 0–10 mg L−1) of cerium standard solution (by Sigma Aldrich, Milan, Italy). The limit of detection (LOD) at the operative wavelength of 413.764 nm was 0.01 mg L−1. The precision of the measurements expressed as RSD % for the analysis was always less than 5%.
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4

Zinc Concentration Analysis in Plants

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The 12 remaining plates of each treatment were used for the Zn concentration analysis. To obtain enough material for Zn analysis four randomly chosen AM‐Donor, AM‐Receiver and NM‐Control plants were merged and thus three replicates were analysed for each treatment. The shoot of each plant was rinsed in a 1 mM CaCl2 solution to remove the Zn adhering to the surface (Yilmaz et al., 2017 ). Zinc concentration was determined by inductively coupled plasma optical emission spectroscopy (ICP‐OES) on an Optima 8000 spectrometer (Perkin Elmer, Waltham, MA, USA), following the procedure of Nölte (2003 ). Zinc concentration was also analysed in the MSR ‐Zn medium collected from both compartments of each treatment. However, it was not possible to analyse Zn concentration in the AM fungal mycelium of both compartments due to weight limitation.
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5

Quantitative Assessment of Heavy Metals

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Quantitative assessments of cadmium (Cd) and copper (Cu) were performed for all the examined species. Amounts of HMs were measured in two replicates (n = 2 samples × 10 species). Foliage, including accumulated PM (these samples were not used for PM analysis), was collected in the same way as previously described in 2.2. After harvest, the samples were dried at 105°C for 48 h, then ground into a ne powder and placed in paper bags until analysis. Powdered plant material (500 mg) was digested with 9 mL of 65 % v/v HNO 3 in Titan MPS (PerkinElmer, Waltham, USA) and diluted to 50 mL.
Samples were then analysed with the high-resolution ICP-OES technique using an Optima 8000 spectrometer (PerkinElmer, Waltham, USA).
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