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Ice 3000 series aa spectrometer

Manufactured by Thermo Fisher Scientific
Sourced in United States, United Kingdom

The ICE 3000 series AA spectrometer is an atomic absorption spectroscopy instrument designed for elemental analysis. It features a double-beam optical system and can detect a wide range of elements in various sample matrices.

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10 protocols using ice 3000 series aa spectrometer

1

Flame Spectrometry for Sodium and Potassium

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The concentrations of excreted sodium and potassium were determined by flame spectrometry (iCE 3000 series AA spectrometer; Thermo Fisher Scientific, Cambridge, UK).
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2

Mineral Content Analysis of Ash Samples

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Ash values were obtained by the calcinations method as described above. After that, 5 mL of nitric acid 0.1M was added and the mixture was stirred on a heating plate to almost complete dryness. Then, 10 mL of the same acid was added and the mixture was made up to 25 mL with ultrapure water [6 ]. The mineral components were determined by atomic absorption spectrometry (Thermo Scientific ICE 3000 Series AA Spectrometer, ISBS Tunisia) after calibrating the instrument, using K (0.1–5 mg/L), Na (0.1–5 mg/L), Ca (0.1–5 mg/L), Mg (0.1–5 mg/L), Fe (0.1–5 mg/L), Cu (0.5–4 mg/L), Zn (0.1–2 mg/L), Pb (0.1–4 mg/L), Co (0.1–5 mg/L), Cd (0.1–2 mg/L), and Ni (0.1–5 mg/L).
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3

Quantitative Determination of Chromium in Plants

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The seedlings were uprooted from media after ten days of growth with intact roots. To avoid Cr cross-contamination from media while uprooting, the seedlings were washed with autoclaved double distilled water. The sample was then kept in a hot air oven at 70 °C overnight for drying. The dry tissue of the sample (100 mg) was digested for an overnight in a 1:1 solution of HNO3 and H2O2 [33 (link)]. The digested sample was then filtered through Whatman filter paper no. 41. The filtrate was allowed to evaporate by incubating at 90 °C using water bath. Then, the remaining filtrate was diluted to make a 6 ml volume with 5% HNO3 solution. Finally, the samples were filtered twice before measuring the absorbance at 357.8 nm in the Thermo Fisher Scientific iCE 3000 series AA spectrometer with acetylene flame. The calibration curve was prepared with chromium standard of required concentration.
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4

Quantification of Oxyfluorfen and Copper in Environmental Samples

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The water samples for oxyfluorfen quantification were concentrated via solid phase extraction (SPE) according to [53 (link)]. Moreover, oxyfluorfen was quantified on tissues according to the method described in [54 (link)]. Then, oxyfluorfen concentrations on water and tissue were achieved via gas chromatography equipped with an electron capture detector (GC-ECD), namely Agilent 7890 B (Wilmington, DE, USA); the procedure was based on the method described in [55 (link)]. The detection limit (LOD) was 3.53 μg L−1 and the quantification limit (LOQ) was 10.68 μg L−1.
Regarding Cu quantification, the preparation of water and tissue samples was performed according to the procedure described in [56 (link)]. Briefly, water samples were acidified with supra pure nitric acid Pro Analysis MERCK® (65%) (Algés, Portugal) to a pH below 2 and stored at 4 °C until the chemical analyses, and the tissues were dried, weighed and digested with nitric acid; after, the organic matter was destroyed with hydrogen peroxide. Cu concentrations were measured via flame atomic absorption spectrophotometry (ICE3000 Series AA Spectrometer—Thermo Scientific—Winsford Cheshire, UK). The LOD was 6.60 μg L−1 and the LOQ was 19.99 μg L−1.
The measured concentrations of each pesticide are presented in Table 1.
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5

Mineral Analysis of Honey Samples

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We added 5 mL of 0.1 M nitric acid to the honey, and the mixture was stirred on a heating plate until nearly dry. Subsequently, an additional 10 mL of the same acid was added, and the mixture was adjusted to a total volume of 25 mL with ultrapure water [50 (link)]. The mineral components were determined using atomic absorption spectrometry (Thermo Scientific ICE 3000 Series AA Spectrometer, Waltham, MA, USA). Prior to analysis, the instrument was calibrated with known concentrations of K (0.1–5 mg/L), Na (0.1–5 mg/L), Ca (0.1–5 mg/L), Fe (0.1–5 mg/L), Cu (0.5–4 mg/L), Zn (0.1–2 mg/L), Pb (0.1–4 mg/L), Cd (0.1–2 mg/L), and Ni (0.1–5 mg/L).
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6

Atomic Absorption Spectrometry Protocol

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Atomic Absorption spectrometer (iCE 3000 SERIES AA Spectrometer, Thermo Scientific, Waltham, USA), fumes chamber/hood (Airflow monitor 100, England), VP 100 Vapor System (VP100, Thermo Scientific, China), electronic balance (ATX224-Shimadzu, Kyoto-Japan), mortar and pestle, laboratory test sieve (Endecotts LTD, London. England), beaker, volumetric flask, conical flasks, water bath, funnel, measuring cylinder and micro pipette.
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7

Comprehensive Soil and Waste Analysis

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Prior to the substrate preparation, 15 single samples of soil and shrimp biowaste were collected. They were pooled and used to determine pH in H 2 O with a potentiometric method and CP-315M meter, and salinity with a conductometric method and CC-411 m. Our analyses also determined the content of N, P, K, Ca and Mg. Total nitrogen was determined according to Kjeldahl method following the sample mineralization in concentrated sulfuric acid and with addition of selenium mixture, total phosphorus levels were measured with colorimetric method according to Egner-Riehm, potassium and general calcium by flame photometry, and magnesium by atomic absorption spectrometry (Thermo scientific iCE 3000 series AA spectrometer) following sample mineralization in 1:1 mixture of nitric and chloric acids. pH and salinity were measured in the substrates before planting and at the end of the growing season in both years.
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8

Metabolic Cage Urine Analysis

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Mice were placed in metabolic cages (food and water ad libitum) for a 24-hour urine collection. Urine sodium and potassium excretion were determined by flame spectrometry (iCE 3000 series AA spectrometer; Thermo Fisher Scientific). The glucose excretion was measured using a colorimetric assay (Cayman Chemical Co).
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9

Cadmium Quantification and Morphological Assessment in B. juncea

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The cadmium standard curve (Abs = 0.46900C + 0.019858, R2 = 0.997) was plotted using the Cd standard solution. B. juncea roots and leaves were prepared and digested according to the approach of Jiang et al. [40 (link)] and the Cd content was determined by Thermo Scientific iCE 3000 Series AA Spectrometers with three biological replicates. Thirty plants were randomly selected from each treatment group to measure the shoot height and root length with a ruler according to Ling et al. [89 (link)]. The dry weights of aboveground and underground parts were measured respectively according to Matse et al. [90 (link)]. Cut off the plant at the base of the stem with a blade and put it into an oven to dry to constant weight. Use an analytical balance to weigh the dry weight of the aboveground part and the underground part, respectively. The cell activity of root tip was determined by Evans blue staining according to Liu and Lin [91 ]. The root tip material was stained with 0.25% (w/v) Evans blue for 24 h, and photo-graphed under stereometric microscope. The data were analyzed by ANOVA using origin 9.1 software. The differences at p < 0.05 were shown to be significant by the LSD test.
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10

Cadmium Quantification in B. juncea Leaves

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B. juncea leaves were digested based on the method of Jiang, et al. [88 (link)], and the Cd content was assayed by iCE 3000 Series AA Spectrometers (Thermo Scientific, USA) with three biological replicates. The Cd standard curve (Abs = 0.46900C + 0.019858, R2 = 0.997) was plotted using the Cd standard solution (China national standard sample no. GSB04–1721-2004).
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