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157 protocols using aa 7000

1

Chemical Characterization of Chalks

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Cube-shaped dried calabash chalk was purchased from the local market of Sylhet, Bangladesh. The chemical analysis of the chalk samples was performed at the Bangladesh Council of Scientific and Industrial Research (BCSIR). The samples were oven-dried (electronic oven) at 105°C for 24 h prior to a microwave digestion (Application note: HPR-EN-13, Model: Start D, Milestone, Italy). Chemical constituents of the chalk were analyzed by Atomic Absorption Spectrophotometer (AAS; Model: AA 7000, Shimadzu, Japan) with a direct Air-Acetylene Flame Method for Mg, Ca, Mn, Cu, Zn, Cd, Fe, Al, Cr, and Pb. Potassium (K) was analyzed by Flame Photometer (Model: PFP 7, Jenway, UK). Arsenic (As) was analyzed by Continuous Hydride Generation Atomic Absorption Spectroscopy (Model: AA 7000, Shimadzu, Japan) with HVG (Hydride Vapor Generator, Model: HVG-1, Shimadzu, Japan) Unit; and the analysis of mercury (Hg) was done by Cold-Vapor Atomic Absorption Spectrometric Method (Model: AA 7000, Shimadzu, Japan) with MVU (Mercury Vaporizer Unit, Model: MVU-1A, Shimadzu, Japan). Methods by the Soil Science Society of America (SSSA) were followed for all the tests [17 (link),18 (link),19 (link),20 (link),21 (link),22 (link)].
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2

Trace Metals Analysis in Soil Extracts

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Eight (8) trace metals, namely-Pb, Ni, Cd, Cu, Cr, Fe, Mn, and Zn, were determined in both extracts by an atomic absorption spectrophotometer (AAS) equipped with a highly sensitive background correction system (SHIMADZU, AA-7000, Japan) at the Department of Agricultural Chemistry, Bangladesh Agricultural University, Mymensingh-2202, Bangladesh. Thousand (1000) µg mL-1 stock solution, which was provided by Sigma-Aldrich, USA, was used to prepare standard series solutions for all trace metals. The instrument′s lowest detection limit for all trace metals was 0.01 µg g-1. Details of calibration of AAS during operations are presented in Table 1 (Suppl.). However, the determinations of soil physicochemical properties viz. pH, EC and organic carbon (OC) were accomplished following the methods mentioned by Tandon18 .
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3

Zinc Content Determination in Plants

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Harvested plants were washed with distilled water and oven dried at 60 °C. Sample preparation for Zn estimation was performed by digesting the plant material in HClO4: HNO3 (1:3, v/v) at 90 °C and then diluting the samples with distilled water. Zinc contents in digested samples were determined on a flame atomic absorption spectrophotometer (AA-7000, SHIMADZU).
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4

Elemental Analysis by Atomic Absorption

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Iron, manganese, chromium, copper, lead, zinc, and calcium contents were determined by atomic absorption spectroscopy (AA-7000, Shimadzu, Japan) after mineralization with 65% hydrogen nitrate (Tendekayi et al., 2011 ). In order to avoid phosphate and ionization interference, the hydrolysis solution was diluted with 10% lanthanum chloride for the determination of calcium content.
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5

Mineral Content Analysis of Solanaceae Plants

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The standard protocol proposed by Moniruzzaman et al. (2014) was used for the determination of mineral ion contents in Solanaceae plants. One gram of air-dried sample was crushed and digested using Nitric Acid (HNO3) and Hydrogen Peroxide (H2O2) in a 5:1 ratio until it became crystal clear. The clear sample was cooled and diluted with distilled water to make up to 50ml. The diluted solution was filtered using a 0.2-micron membrane filter and analysed for detection of elements using Atomic Absorption Spectroscopy (Shimadzu AA-7000, Japan) and Microwave Plasma Atomic Emission Spectroscopy (4100 MP-AES, Agilent Technologies, USA).
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6

Macro- and Micronutrient Analysis of Plant Samples

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Dried shoot and root samples of the three plants that were randomly selected from each treatment were ground separately, and their macro- and micronutrient concentrations were analyzed. Nitrogen and P concentrations were determined using the Kjeldahl method and ammonium molybdate blue method, respectively (Allen, 1989 ), whereas K+, Na+, Ca2+, Mg2+, Fe2+, Zn2+, and Mn2+ concentrations were measured following the methods described by Colla et al. (2008) (link) using an atomic absorption spectrophotometer (AA7000; Shimadzu, Tokyo, Japan).
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7

Elemental Analysis of Metal Samples

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Elemental Analysis was performed by ICP-AES, AAS, and complexometric titration.
ICP-AES analysis was carried out using inductively coupled plasma atomic emission spectrometer Prodigy High Dispersion ICP (Teledyne Leeman Labs., Hudson, NH, USA).
Elemental analysis was carried out using atomic absorption spectrophotometer AA-7000 (Shimadzu, Kyoto, Japan) at 213.9 nm. The samples were pretreated with HNO3:HClO4 (6:1) to leach out zinc metal.
Complexometric titration was performed in accordance with the European Pharmacopoeia (2.5.11).
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8

Silver Ion Quantification in Tissues

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Silver ion concentration was determined in different organs after the administration of CS-AgNPs in similar dosing scheduled used for toxicity studies according to the method reported by Lee et al in 2013.37 (link) The animals were sacrificed after 28 days, and tissues were digested in nitric acid using a multiwave microwave digester (Anton Paar, USA). The atomic absorption (AA) spectrophotometer (AA-7000, Shimadzu, Japan) equipped with a graphite furnace (Elmer, USA) was used for the Ag ion determination. The Ag ion concentration in each tissue was calculated in μg/g wet weight. The limit of detection (LOD) and the limit of quantification (LOQ) were found to be 0.29 μg/kg and 0.88 μg/kg, respectively, in the quantification method.
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9

Graphite Furnace AAS for Heavy Metals

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The analysis of heavy metals was done using the graphite furnace atomic absorption spectrometry method (AA-7000, Shimadzu, Japan) in the laboratories of the Iraqi Ministry of Science and Technology.
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10

Quantification of Macro and Micronutrients

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In the case of P, 0.5 mL of the sample was taken and 4 mL of water Type I and 0.5 mL of ammonium molybdovanadate 1% solution were added. The sample was stirred and the absorbance was measured in a UV-Visible spectrophotometer (UV2600, Shimadzu, Tokyo, Japan). Quantification was based on a calibration curve, and the results were expressed in mg 100 g−1 of dry weight sample.
For the analysis of macronutrients, an aliquot of 4.5 mL of sample was taken in a test tube, 0.5 mL of lanthanum 1% solution was added for determination of Ca and Mg. In the case of Na and K, 0.5 mL of lithium 1% solution was added in the same volume of sample and to eliminate interferences.
For the analysis of micronutrients (Zn, Cu, Fe, and Mn), 5 mL of each sample was taken and no solutions were added for interferences. In the prepared samples, the absorbance was measured in an atomic absorption spectrophotometer (AA7000, Shimadzu, Tokyo, Japan). S and B content were measured directly from the solutions of each sample in an inductively coupled plasma spectrophotometer (5300 Optima DV, Perkin Elmer, Bresia, Italy). The quantification was carried out using calibration curves for each element; the results were expressed as mg 100 g−1 of dry weight sample.
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