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Aanalyst 200

Manufactured by PerkinElmer
Sourced in United States

The AAnalyst 200 is a versatile atomic absorption spectrometer designed for elemental analysis. It features a double-beam optical system and a high-performance deuterium background corrector for accurate measurements. The AAnalyst 200 is capable of analyzing a wide range of sample types and can detect low concentrations of various elements.

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88 protocols using aanalyst 200

1

Characterization of Santiago River Sediments

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The samples of sediments from the Santiago River (SRS) were characterized by measuring the following parameters in situ using a YSI 1725 water quality meter: pH, oxidation–reduction potential (ORP), electric conductivity (EC), salinity, and total dissolved solids (TDS). Chemical oxygen demand (COD), total organic carbon (TOC), total solids (TS), and volatile solids (VS) were determined in laboratory facilities using colorimetric Hach probes for the first two (2125915 LM, 2815945, respectively) in DR900, and the gravimetric technique for the last two. Dissolved oxygen was measured using an electrode.
For heavy metal determination, atomic absorption spectrophotometry equipment PerkinElmer AAnalyst 200 was used. The sediment sample was ground and preserved by adding nitric acid until it reached a pH of less than 2 and kept at 4 °C until analysis. Three sample replicates were filtered, and residues were vacuum-dried and sieved to a particle size of 2 mm. A mixture of HCl:HNO3 at a 1:3 ratio was used for digestion using an autoclave. Concentrations were interpolated using high-purity NIST-traceable standards. For the determination of arsenic, a hydride generator included in the PerkinElmer AAnalyst 200 flame atomic absorption spectrophotometry equipment was used.
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2

Heavy Metal Analysis in Sludge Samples

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Crucibles were rinsed with deionized water and then heated at 105 °C and put into the ashing furnace at 600 °C for 2 to 4 h. The sludge samples were ashed in triplicates by placing them into the ashing furnace at 600 °C for 6 to 8 h. The samples were mixed and heated with 5 mL of 3N HCl (Fisher Scientific, UK) until the solid samples were completely dissolved in an HCl solution. When the mixture of samples and HCl was cooled down to room temperature, the mixture was filtered with filter paper (Advantec No.1 125 mm, Toyo Roshi Kaisha, Ltd., Tokyo, Japan) and prepared in a 100 mL volumetric flask for further analysis of heavy metals using a flame atomic absorption spectrometer (AAnalyst 200, PerkinElmer, Inc., Waltham, MA, USA).
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3

Liposomal Encapsulation Efficiency Determination

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A specific volume (5 mL) of the liposomal dispersion was subjected to a high-speed centrifugation at 21,000 rpm at 15°C for 120 minutes. The sediment was redispersed in 5 mL of isotonic phosphate buffer. The centrifugation was repeated twice. The liposomes were separated from the supernatant. One mL of the prepared liposomes was diluted and adjusted to a volume of 5 mL with methanol in a 10 mL volumetric flask, and the amount of the encapsulated drug was determined spectrophotometrically at a λ of 276 nm, respectively. The amount of the encapsulated gold nanoparticles was determined using an atomic absorption spectrometer (AAnalyst 200; PerkinElmer Inc., Waltham, MA, USA) at a wavelength of 243 nm, where the samples were processed at 120°C in diluted aqua regia in an oil bath for 1 hour.25 (link)
The percentage of entrapment efficiency was calculated using the following equation:
EE%=TDUEDTD×100 where EE % is the encapsulation efficiency percentage, TD is the total drug amount, and UED is the amount of unencapsulated drug.
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4

Cesium and Potassium Quantification in Plantlets

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At least three biological replicates, consisting of 60–72 pooled seedlings in each replicate, were analyzed for each treatment group. Whole eight-day-old plantlets were harvested, rinsed in Milli-Q water, and dried in an oven at 65 °C for 3~4 days. Two ± 0.1 mg samples of dried seedlings were extracted in 1 mL of 60% (v/v) HNO3 by heating at 125 °C for 1 h. The resulting solutions were then diluted with Milli-Q water to 10 mL. Cesium and potassium levels were measured by an AAnalyst 200 flame atomic absorption spectrometer (PerkinElmer) or an inductively coupled plasma mass spectrometry (NexION® 300 ICP-MS System, PerkinElmer, Waltham, MA, USA). The concentrations of the elements were calculated against a standard curve constructed for each element [72 (link)]. Statistically significant differences between treatment groups or plant lines were evaluated with a one-way ANOVA with Bonferroni’s multiple comparison post-test using GraphPad Prism software (version 5, GraphPad Software, La Jolla, CA, USA).
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5

Analyzing Forest Soil Physicochemical Properties

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The organic layer (forest floor) was sampled within a 25 × 25 cm square using a metallic frame. The composite samples of the forest floor were obtained from four subsamples (n = 4), oven-dried at 105 °C to a constant mass, and weighted. Mineral soil was sampled from 0–10 cm by a metallic soil auger in August–September 2020. Four composite samples were combined from 10 subsamples collected systematically in each sample plot. The forest floor and mineral soil samples were analysed for pH, which was determined in a 0.01 M CaCl2 suspension (ISO 10390:2005); organic carbon (Corg) was determined using a dry combustion method with a total carbon analyzer Analytic Jena multi EA 4000, Jena, Germany, and total nitrogen (N) by the Kjeldahl method (ISO 11261). The concentration of mineral N was determined by the spectrometric method (ISO 14256-2) in 1 M KCl extraction. Soil available K2O and P2O5 were determined in ammonium lactate-acetic acid extractant [62 ] by the Shimadzu UV 1800 spectrophotometer (Shimadzu, Kyoto, Japan) and JENWAY PFP7 flame photometer, respectively. Soil available Ca and Mg were determined by atomic absorption spectrometer AAnalyst 200 (PerkinElmer, Waltham, MA, USA) (laboratory method LVP D-13:2016).
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6

Foal Feces Analysis for Nutrient Determination

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Foal feces at 12 h, 2, 3, 5, 7, 10, 14, and 21 d were dried to a steady state in a 55 °C forced-air oven, then ground in a Cyclotec Sample Mill (Foss, Hillerod, Denmark). Dried ground samples were used to determine NDF and chromic oxide content. Fecal NDF was determined using an Ankom 200 Fiber Analyzer (Ankom Technology, Macedon, NY, USA) following the manufacturer’s instructions. To analyze the chromic oxide concentration in fecal samples, a 0.5 g sample of dried, ground feces was placed in a quartz crucible and ashed at 600 °C overnight. The samples were then digested using potassium bromate and manganese sulfate. Digested samples were placed in specimen cups and then diluted to 100 mL with a calcium chloride solution and allowed to stand overnight. The chromium in the solution was analyzed using atomic absorption at a wavelength of 357.87 nm (AAnalyst 200, PerkinElmer Inc., Waltham, MA, USA) and the concentration was calculated using a six-point standard curve (1–7 ppm).
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7

Elemental Analysis of Plant Samples

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Three biological replicates of whole, 8-day-old plantlets (40–60 seedlings pooled per replicate) were collected, rinsed in Milli-Q water, and dried in an oven at 65 °C for 3–4 days. Subsequently, 2 ± 0.1 mg of dried sample was weighed and extracted as described in our previous study17 . The concentrations of K and Cs were determined with a flame atomic absorption spectrometer AAnalyst 200 (PerkinElmer) or by inductively coupled plasma mass spectrometry (NexION® 300 ICP-MS System, Perkin Elmer, Waltham, USA). The concentrations of K and Cs were calculated based on standard curves generated for each element. Statistical differences between sample means were evaluated with a one-way ANOVA followed by a Bonferroni’s multiple comparisons test using Prism software version 5 (GraphPad Software, San Diego, USA).
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8

Comprehensive Water Quality Analysis

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For the determination of physical and chemical parameters, sulfate (SO4), nitrate (NO3), phosphate (PO4), ammonia (NH3), calcium (Ca), iron (Fe), magnesium (Mg) and manganese (Mn) were analyzed in the samples. The concentrations of some potentially genotoxic heavy metals cadmium (Cd), chromium (Cr), arsenic (As), nickel (Ni), copper (Cu), cobalt (Co), mercury (Hg), zinc (Zn) and lead (Pb) were analyzed using an atomic absorption spectrophotometer (Perkin Elmer A Analyst 200), and PAHs and benzene were measured according to standard analytical methods.9–10
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9

Leaf Nutrient Analysis Protocol

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Each July, samples of about 100 fully expanded leaves from the current season’s growth of shoots without fruit (diagnostic leaves) were collected from each measured tree. The leaf samples were rinsed in deionised water, oven-dried (70 °C), ground to a powder, and 0.1 g were digested with sulfuric acid and hydrogen peroxide (Merck, Darmstadt, Germany) [67 ]. The P and N content was determined by colorimetric analysis (Gallery Plus Automated Photometric Analyzer, Thermo Scientific, Waltham, MA, USA). The K content was determined using an atomic absorption spectrometer (AAnalyst 200, Perkin-Elmer, Waltham, MA, USA). Fruit samples collected at harvest were crushed to paste and handled similar to the leaf samples.
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10

Quantification of Sodium, Potassium, and Chloride Ions

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For the quantification of Na+ and K+, between 50 and 100 mg of dried material was weighed in 2 mL tubes. One millilitre of ultrapure water (Fluka Analytical, Sigma-Aldrich, USA) was added and the tubes were boiled for 10 min at 100 °C. Samples were then filtered in a 96-wells filter plate (Thermo Scientific, Rochester, NY, USA) through centrifugation at 3000 rpm for 3 min. For Na+ and K+ measurements, 6 µL of the filtrate was diluted in 6 mL of ultrapure water (Fluka Analytical, Sigma-Aldrich), and the resulting solution was analysed for Na+ and K+ concentrations using an atomic absorption spectrometer (AAnalyst 200; PerkinElmer AAS). The AAS was calibrated using sodium and potassium atomic spectroscopy standard concentrate (Fluka Analytic, Sigma-Aldrich), and the average of three technical replicas was used for the ion concentration calculations. Cl ions were measured directly on the filtered samples, also used for Na+ and K+ measurements, on a chloride counter (MKII Chloride Analyzer 926; Sheerwood, UK). The chloride counter was calibrated with 500 μL of Chloride Meter Standard (Sheerwood).
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