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Optima 3000

Manufactured by PerkinElmer
Sourced in United States

The Optima 3000 is a compact, fully automated benchtop inductively coupled plasma (ICP) optical emission spectrometer (OES) system designed for routine elemental analysis. It offers precise and accurate multi-element quantification of a wide range of sample types.

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26 protocols using optima 3000

1

Characterization of Er3+ and Yb3+ Doped Na5Lu9F32 Crystals

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X-ray diffraction (XRD) of the samples was measured using a D8 Advance diffractometer (BRUKER, German). The absorption spectra were recorded with a Cary 5000 UV/VIS/NIR spectrophotometer (Agilent Co., America). The emission spectra were obtained with a FLSP 920 type spectrometer (Edinburgh Co., England). The external quantum efficiency were measured by a fluorescence spectrometer (FLS 980) of Edinburgh instruments combined with an integrating sphere. All the measurements were measured at room temperature. The actual concentrations of Er3+ and Yb3+ ions in all the samples were measured by an inductively coupled plasma atomic emission spectroscopy (ICP-AES, Perk in Elmer Inc., Optima 3000). The measured Er3+ and Yb3+ concentrations in all crystals are presented in Table 1.

The measured molar concentrations and the number of Er3+ and Yb3+ in Na5Lu9F32 crystal.

SamplesEr3+Yb3+
Molar concentration (mol%)The number of ion(1020 ions/cm−3)Molar concentration (mol%)The number of ion (1020 ions/cm−3)
NFEY10.981.51200
NFEY20.991.5031.971.978
NFEY61.011.5025.996.028
NFEY80.991.5067.978.02
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2

Evaluating Antifouling Agent Release Kinetics

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To evaluate AF release, AF-NP gel or free AF-NPs were loaded into dialysis cups (10 kDa cutoff; Slide-A-Lyzer™ MINI Dialysis Devices) and dialyzed at 37℃ against 2 L of phosphate-buffered water (pH of 7.0 or 4.5). The buffer was changed every 2 h for the first 12 h. At various time points, the amount of NP-associated AF remaining in the cups was determined by ICP-OES (Perkin Elmer Optima 3000) or HPLC. For ICP-OES, NPs were dissolved for 2 h in aqua regia (hydrochloride acid:nitric acid, 3:1; v/v) to release the gold ion, followed by acid removal through overnight heating at 80℃. The crystallized gold salt was dissolved in 5 mL of 2% nitric acid, and the gold content was analyzed by ICP-OES based on the gold emission line at 242.8 nm. For HPLC, NPs were dissolved in acetonitrile for 3 h. For both assays, AF amounts were derived from standard curves.
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3

Elemental Analysis of Plant Leaves

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For ion analysis, finely ground samples of lyophilized leaves were digested in a microwave oven (CEM Mars Xpress, North Carolina, USA), by HNO3 : HClO4 (2 : 1) digestion. The elements were detected by inductively coupled plasma (ICP) analysis (Optima 3000, PerkinElmer).
The concentrations of ions in the vesicles were determined after centrifugation of the vesicle preparations. The pellets obtained were dried and digested and the ions were determined by ICP, as described previously.
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4

Comprehensive Faecal and Urine Analysis

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Faeces and urine of Studies 1, 3 and 4 were analysed as described previously (except neutral sterols and bile acids) [11 (link),19 (link),20 (link)]. In Study 2, mineral concentrations in faeces were determined following pressure digestion using ICP-OES (Optima 3000, Perkin Elmer, Waltham, MA, USA).
Faecal neutral sterols (cholesterol and its metabolites coprostanol, coprostanone, cholestanol, cholestanone, and cholestenone) and bile acids (iso-lithocholic acid: iLCA, lithocholic acid: LCA, iso-deoxycholic acid: iDCA, deoxycholic acid: DCA, cholic acid: CA, chenodeoxycholic acid: CDCA, and 12keto deoxycholic acid: 12keto DCA) were analysed as described previously [22 (link)]. Briefly, neutral sterols were extracted with cyclohexane following a mild alkaline hydrolysis. Analysis was performed by GC-FID (GC17A-AF Vers. 3, Shimadzu, Kyoto, Japan). Bile acids were extracted with diethyl ether following a strong alkaline hydrolysis. Thereafter, extracts were methylated, silylated, and analysed by GC-MS (GC17-QP5000, Shimadzu, Kyoto, Japan).
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5

Peroxide Bleaching of Pulp with Transition Metal Removal

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The peroxide bleaching was done after removing transition metal by the complexing treatment (Q-stage). The Q-stage was performed using 0.3% diethylenetriamine penta acetic acid (DTPA) and 1 mol l−1 H2SO4 at 65 °C for 60 min to remove transition metals.35 (link) The metal content in the pulp before and after Q-stage was analyzed by ICP-OES (Optima 3000, PerkinElmer) after hydrolysis with nitric acid in a microwave oven, according to Janzon et al.36 (link)All peroxide bleaching stage was made at 70 °C for 2 hours. The peroxide/NaOH concentrations were 4%/2% (P1), 2%/1% (P2) and 3%/1.5% (P3). At the end of the stage, the pulp was washed and air-dried for analysis based on Section 2.4.
Chlorine dioxide was also used as the last bleaching stage for (OQP2D) bleaching sequence. The pulp consistency of 7% and chlorine dioxide concentration of 0.4% was used for the chlorine dioxide stage.
The final pulp brightness, viscosity and kappa number were analyzed after each bleaching sequence.
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6

Olive Leaf Elemental Analysis Protocol

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At the end of the experimental period, the olive shoots were collected, and the leaves from the different treatments were first washed in distilled water. This washing liquid was analysed by ICP-OES and liquid chromatography, as described below, for determining the leaf surface K and anion concentrations.
For tissue elemental analysis, pre-washed olive leaves (i.e., after the preliminary water described above) were subsequently washed in a 0.1% detergent (Fairy, P&G), acidulated solution (0.1 N HCl). The plant tissues were then rinsed twice in tap water, and then in distilled water, and were consequently oven-dried at 70 °C for two days, then weighed and ground prior to mineral element determination after dry-ashing. The concentration of nutrients in the plant tissues was detected by inductively coupled plasma (ICP, PerkinElmer, Optima 3000), following the UNE-EN ISO/IEC 17025 standards for calibration and testing laboratories (CEBAS-CSIC Analysis Service, Murcia, Spain). On the other hand, the anions were analysed by liquid chromatography (CEBAS-CSIC Analysis Service, Murcia, Spain), after the extraction of approx. 0.3 g dry weight (D.W.) of leaf tissue in distilled water for 2 h, and centrifugation and filtration with 0.45 µm filters.
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7

Sediment Elemental Analysis Protocol

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Approximately 125 mg of freeze-dried sediment was dissolved in 2.5 ml of HF (40%) and 2.5 ml of HClO4/HNO3 mixture in a closed Teflon bomb at 90°C during one night. The acids were then evaporated at 160°C, and the resulting gel was subsequently redissolved in 1 M HNO3 at 90°C during another night. Subsequently, total elemental concentrations were determined by inductively coupled plasma optical emission spectrometry (PerkinElmer Optima 3000). Precision and accuracy were better than 5%, based on calibration to standard solutions and checked against internal laboratory standard sediments.
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8

Metal Binding Assay of EfeM Protein

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The detection of metals in the apo-and metal-incubated forms of purified EfeMPsy was performed by ICP-OES, using the instrument PERKIN-ELMER Optima 3000. The metal stock solutions were prepared by dissolving the chloride salts of each metal tested in 30 mM MES, pH 6.0. In the case of ferrous iron, the stock solutions were prepared in 30 mM MES, pH 5.0, to reduce oxidation of the ferrous iron. The proteins (2–50 µM) were incubated with 0.25 mM metal stock solution separately (Cu2+, Zn2+, Fe2+, Mg2+, Mn2+ and Fe3+) at 4 °C for 1 h. The unbound metals were then removed by subjecting the incubated samples to dialysis, using 12 kDa MWCO dialysis tubing against metal-free buffer (30 mM MES, pH 6.0 or pH 5.0) with the replacement of buffer every 8 h three to four times to remove the unbound metals. In the case of the Fe2+ binding experiments, to prevent oxidation the buffer pH was maintained at 5.0 and nitrogen gas was bubbled/purged into the dialysis system at regular intervals.
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9

Quantitative Elemental Analysis Protocol

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Metallic elements were determined using the PerkinElmer Optima 3000 emission spectrometer that can measure wavelengths between 167–782 nm for over 5000 emissions. The liquid sample was rapidly atomized using an argon plasma at 7000 °C and electrons excited for detection and analysis using WinLab32 software. The non-metallic elements were analysed using the Vario EL Elementar equipment. It was conducted in accordance to the Petrochemical industry standard GB/T 19143-2003.
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10

Elemental Analysis of Leaf Samples

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For an ionic analysis, the leaves were washed well with distilled water and lyophilized. Finely ground samples of lyophilized leaves were digested in a microwave oven (CEM Mars Xpress, Matthews, NC, United States) by HNO3:HClO4 (2:1) digestion. The elements were detected by an inductively coupled plasma (ICP) analysis (Optima 3000, PerkinElmer, Norwalk, CT, United States).
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