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Novaa300

Manufactured by Analytik Jena
Sourced in Germany

The NovAA300 is an atomic absorption spectrometer manufactured by Analytik Jena. It is designed for the analysis of trace elements in various sample types. The instrument utilizes the atomic absorption technique to determine the concentration of specific elements in a sample.

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15 protocols using novaa300

1

Optimizing Selenium Uptake by Fungus

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Different concentrations of sodium selenite (Na2SeO3) (2, 4, 6 and 8 mg/L) were added to the substrates. After incubation, the mycelia of A. cylindracea were collected and weighed to obtain the best concentration. The mycelia were filtered and washed three times with deionized water, followed by constant drying at 50°C to measure the biomass (g/L). The mycelia (0.1 g) were nitrified through the addition of 2 mL of perchloric acid and 8 mL of nitric acid at room temperature for 12 h. The final 2 mL of nitrification liquor, determined through continuous heating, was mixed with 23 mL of double-distilled water for further flame atomic absorption spectrometry analysis (FAAS, nov AA® 300, Analytik Jena AG, Jena, Germany).
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2

Zinc Content Determination by AAS

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MPS and MZPS (0.1 g) were weighed severally, and then added 5 mL HNO3 and 2 mL HClO4 and let the mixture standing overnight. The mixture was boiled until the cooking liquor clear. After digestion of the samples, the mixture was diluted to 25 mL. The zinc content was measured by using flame atomic absorptions spectrometric method (novAA300, Analytik-Jena, Germany).
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3

Soil Physicochemical Characterization

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The soil physicochemical characteristics of each treatment were measured following the methods described by Bao (2000) . Soil pH was measured using a suspension of soil and deionized water at a ratio of 1:2.5 (w/v). Soil total C, N, H, and S contents were determined separately using an elemental analyzer (Flash EA 1112, Thermo Finnigan). DOC and DON were measured using a TOC analyzer (Multi N/C 3100, Analytik Jena AG). Soil exchangeable Na+, K+, Ca2+, and Mg2+ were extracted with 1M ammonium acetate from the bulk soil in unplanted treatments and from the rhizosphere soil in the planted treatments. Extracts were measured by atomic absorption spectrophotometry (NovAA300, Analytik Jena AG). NO3-N, NH4+-N, and CEC were measured in a continuous colorimetric flow system (Skalar SAN++ System, Netherlands).
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4

Quantifying Mercury and Aluminum in Zebrafish

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Total Hg and Al were determined in Danio rerio’s head and body by atomic absorption spectrometry (AAS) with atomization in a graphite oven (GF-AAS) and cold steam (CV-AAS) using Analytik Jena spectrometers (NovAA 300 models with hydride generator module HS60 and ContrAA 700). The analyzed samples underwent pre-treatment for total digestion in a microwave oven (Anton Paar brand, Graz, Austria). The samples were digested by acid using the oxidant mixture HNO3 + H2O2 according to the EPA3050B reference method described by the EPA [47 ]. After total digestion, the samples were diluted to 25 mL in ultrapure water (Milli-Q) and analyzed according to the methodologies validated for each element. For the determination of total Hg, mol/L HCl and NaBH4 (0.25% w/v) solutions were used as acidic and reducing media, respectively. Hollow cathode lamps were operated at 4 mA. The wavelength was set to 253.7 nm for Hg and 309.3 nm for Al, and the spectral band passes at 0.5 nm for both metals. The final concentration of each element was calculated in µg/g according to the wet mass used in each digested sample (~300 mg).
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5

Soil Chemical Characterization Methods

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Soil pH was determined by a combination of glass electrodes using a 1: 2.5 (w: v) ratio of soil to distilled water (Mi et al., 2018 (link)). Soil total C (TOC) and N (TON) were measured by LECO CNS Combustion Analyzer (LECO, CNS 2000, LECO Corporation, Michigan, United States) following manufacturer protocol. Available phosphorus (AP) in soil was determined by ammonium fluoride extraction (Bray and Kurtz, 1945 (link)). Soil available K+, Ca2+, and Mg2+ were extracted using 1 M KCl (1:10), and determined by using atomic absorption spectrophotometry (NovAA300, Analytik Jena, Germany).
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6

Soil Nutrient Analyses Using Standard Methods

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Soil organic matter was determined using the K2Cr2O7 titration method. Soil available P was extracted with 0.5 M NaHCO3 (pH 8.5) and then determined using the Olsen method [37 ], and soil available K was extracted with 1 M ammonium acetate (pH 7.0), and measured by atomic absorption spectrometry (NovAA300, Analytik Jena AG). The total N content and the atom% 15N of soils and plants were determined using a stable isotope ratio mass spectrometer (Isoprime100 and Vario Pyrd/Cube, Elementar, Germany). Soil mineral N content (Nmin: NH4+-N and NO3-N) was extracted with 1M KCl and determined using a flow injection analyzer (FLA star 5000 Analyzer, Foss, Denmark). Soil microbial biomass N content (MBN) was determined by chloroform fumigation-extraction protocol, extracted with 0.5M K2SO4, and analyzed using a multi N/C analyzer (Multi N/C 3100/HT1300, Analytik Jena AG, Germany). The atom% 15N of Nmin and MBN was determined using a stable isotope ratio mass spectrometer (Isoprime100 and Vario Pyrd/Cube, Elementar, Germany).
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7

Extraction and Quantification of Leaf Iron

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Iron was extracted by soaking 100 mg of dry young leaves in 25 mL of 1 mol mL−1 hydrochloric acid at room temperature for 24 h. Iron concentrations of the extracted samples were measured using an atomic absorption spectrophotometer (NOVAA 300, Analytikjena, Jena, Germany).
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8

Determining Metals in Virgin Coconut Oil

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Acid digestion was used to determine the amount of metals, including lead, copper and iron (Pb, Cu, and Fe), contained in the VCO according the method reported by Ang and Lee (2005). About 0.5 g of VCO was added into 9 ml of freshly‐prepared mixture of HNO3 (63%) and HCl (37%) at 1:3 ratio in a digestion flask. The mixture was boiled gently over a water bath at a temperature of 80–90°C for 4–5 hr until the sample had completely dissolved. Once digestion has completed, the mixture was then cooled down to room temperature and filtered through filter paper (Whatman No. 42; 2.5‐μm particle retention). The extract was then evaporated to remove excessive acid, and the volume was topped up to 50 ml with distilled water. The metals in the VCO were quantitatively measured using Nov AA 300 (Analytik Jena, Germany) atomic absorption spectrometer (AAS). The measurement condition was optimized for the determination of the metals with the limit of detection of 1 μg/l. The standard calibration of the metals was measured from 0 to 10 ppm.
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9

Quantifying Na+ and K+ in Plant Tissues

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For measurement to Na+ and K+. the 3-d-old seedlings grown under normal conditions were transferred to the MS medium containing 0 or 150 mM NaCl and then grown for 2 d. The shoots and roots from these 5-d-old plant were separately harvested, dried for 48 h at 80 °C and then ground to powder. The same mass tissue powder was digested in concentrated (69%, v/v) HNO3 for 24 h at room temperature for elemental extraction. Na+ and K+ concentrations was determined by atomic absorption spectrophotometry (novAA300, analytikjena).
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10

Heavy Metal Remediation via Bacterial Bioaccumulation

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The composition of LB (Luria-Bertani) liquid medium was 5.0 g/L beef extract, 10.0 g/L peptone, 5.0 g/L NaCl, pH 7.0. Taking 79 mL LB liquid medium into each beaker flask, all of the media were autoclaved at 121 °C for 20 min, 1 mL of the logarithmic phase bacteria was added in the liquid medium, the initial optical densities (OD600) were all kept at 0.03, and 10 mL of 20 mM CdCl2·2.5H2O solution and 20.0 g/L of urea solution filtered through 0.22 µm filter were added, respectively. Then, the samples were incubated (170 rpm) at 37 °C for 120 h. Samples were taken at regular time intervals and the pH was measured. The concentrations of Cd2+ in the samples were measured using an atomic absorption spectrometer (novAA300, Analytik Jena AG, Jena, Germany).
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