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Aa700

Manufactured by PerkinElmer
Sourced in United States

The AA700 is an atomic absorption spectrophotometer manufactured by PerkinElmer. It is designed for the quantitative determination of trace elements in various sample types. The AA700 utilizes a specialized light source and detector to measure the absorption of light by atoms in the sample, which allows for the identification and measurement of specific elements.

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12 protocols using aa700

1

Optimizing NMGO Adsorption for Cu(II) and Cr(VI)

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In this work, five factors, namely pH, temperature, initial concentration of metal ions, CaCl2, and HA, were screened for their effects on the adsorption capacities of NMGO for Cu(II) and Cr(VI) ions (response) using a 25−1 FFD with resolution V. The experimental factors and their levels used in the 25−1 FFD were demonstrated in Table 1. The software of Design Expert 8.0.6 (Stat-Ease Inc., Minneapolis, MN, USA) was used for the FFD of the experiments and regression analysis of the obtained experimental data. The full design matrix of the 25−1 FFD is shown in Supplementary Table S4. All adsorption experiments were performed in a 150 mL conical flask containing 50 mL aqueous solution of Cu(II) or Cr(VI), and the samples were agitated at 150 rpm for 24 h in a rotary shaker. Then, the mixture in the conical flask was separated using a permanent magnet. The Cu(II) and Cr(VI) concentrations in the supernatant were analyzed by a flame atomic absorption spectrometry (PerkinElmer AA700, USA) and an UV-visible spectrophotometer (Pgeneral T6, Beijing) at 540 nm, respectively16 (link). The adsorption capacity (qe) of NMGO was calculated from the difference between the initial concentration (C0) and the equilibrium concentration (Ce).
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2

Measurement of Cadmium Accumulation in Plants

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For the measurement of Cd, 0.5 g dried plant material was acid digested using HNO3 (nitric acid) and HClO4 (perchloric acid) in 4:1 ratio at 60 °C by adopting the hot plate block method depicted by Jackson34 . The sample analysis for Cd was conducted through an atomic-absorption spectrophotometer (AAS) (Perkin Elmer AA700, USA). Cadmium translocation factor was determined as per the method of Bose and Bhattacharyya. Bioconcentration factor (BCF) was computed as heavy metal accumulated in each plant tissue to that dissolved in the soil medium as shown below: Shootbioconcentrationfactor:BCFs=Cshoot/Csoil Rootbioconcentrationfactor:BCFr=Croot/Csoil
Translocation factor (TF) of cadmium was computed using the above equations as follows: TF=BCFshoot/BCFroot
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3

Spectroscopic and Microscopic Techniques for Material Characterization

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Fluorescence spectra were obtained using the FP-6500 spectrofluorometer (JASCO, Japan). Fourier transform Infrared spectra (FTIR) were acquired over the range 600–4000 cm−1 using the Tensor 27 FTIR spectrometer (Bruker, Germany), equipped with a germanium-attenuated total reflection (ATR) accessory. The size and morphologies of the as-synthesized samples were investigated via high-resolution transmission electron microscopy (HRTEM) using the JEOL JEM-2010 electron microscope (JEOL, Japan) at the acceleration voltage of 200 kV. Flame atomic absorption spectrometry (Perkin-Elmer, AA700) with an air-acetylene flame was used as the classical reference method to determine Cu2+ in CHMs, and the wavelength was set to 324.8 nm with a spectral slit-width of 0.7 nm and a lamp current of 15 mA. The model T6 UV/Vis spectrophotometer (Beijing Purkinje General Instrument Co., Beijing, China) was used to obtained the absorption spectra. The pH-3C digital pH meter (Shanghai Leici Instrument Factory, Shanghai, China) was used for pH adjustment.
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4

Cadmium Quantification in Plant Tissues

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Dry shoot and root materials (0.1 g) were digested in a mixture of nitric acid and perchloric acid (4:1) using the hot block digestion procedure (overnight at 60 °C) according to the method of Jackson (1962) and described by Burd et al. (2000) (link). After cooling, 1.0 ml of hydrogen peroxide (30%, v/v) was added to the digested sample and incubated for 2 h. The cadmium concentration was measured by an atomic absorption spectrophotometer (Perkin Elmer AA700, USA).
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5

Hexavalent Chromium Adsorption Protocol

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All the chemicals and reagents used were of analytical grade (Kelong Chemical Reagent Factory, Chengdu, China). Potassium dichromate was used as adsorbate. The stock adsorbate solutions (1000 mg l−1 and 5000 mg l−1) were prepared by dissolving 2.828 and 14.140 g of potassium dichromate in 1 l ultrapure water, respectively. All working solutions were obtained by dilution. Cr(VI) concentration was determined by a spectrophotometer according to Chinese National Standard GB/T 7467-87. The total Cr was determined by a flame atomic absorption spectrometer (AA700, Perkin-Elmer, USA). The Cr(III) content was the difference between total Cr and Cr(VI) in the solution.
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6

Regeneration and Reuse of MMC Adsorbent

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To carry out the leaching experiment, 5 mg MMC or P-MMC was dispersed in 10 mL of Cu(II) solutions with different pH. At the specific contact time, the suspension was separated and the leached iron concentration in the supernatant was determined by a flame atomic absorption spectrometer (FAAS, PerkinElmer AA700, USA). The feasibility of regenerating P-MMC for repeated use was investigated by using acidic ethanol. Specifically, after accomplishment of the adsorption experiments, the Cu(II)-loaded (or atrazine-loaded) adsorbent was magnetically separated and subsequently added into 10 mL 20% acidic ethanol for desorption at 150 rpm at 303 K. After washing thoroughly with ultrapure water to neutral pH, the regenerated adsorbent was recycled and reused, and the adsorption performance of P-MMC was investigated again, meanwhile, leached iron concentration in the supernatant was also determined.
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7

Microwave Digestion and AAS for Chromium

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For the Cr estimation, a sample of 0.5 g of dried plant material was acid-digested in HNO3 (70%) using the microwave digestion system 2000, following the procedure as described by Gupta and Sinha [120 (link)]. In dried leaf samples, the Cr content was estimated with the help of an atomic-absorption spectrophotometer (Perkin Elmer AA700, Waltham, MA, USA). The Cr accumulation and translocation were estimated as per Duman et al. [121 (link)].
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8

Determination of Mineral Content

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Hot-water extracts were prepared with homogenized finely ground dry plant material in deionized water at 100 °C (Khan et al. 2000 ) in capped Pyrex test tubes. Soluble Na+, K+, Ca2+ and Mg2+ in shoot and root were determined on dilutions of the hot water extracts by atomic absorption spectrometry (AA-700; Perkin Elmer, Santa Clara, CA, USA).
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9

Measuring Na+ and K+ Concentrations in Populus

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Na+ and K+ concentration in the two Populus species were measured with an atomic absorption spectrophotometer (Perkin-Elmer, AA700, Waltham, MA, USA) using the method described previously [19 (link)]. Leaves of the salt-treated and control plants were oven-dried at 65 °C during more than 3 days to achieve complete dehydration. The dry samples were ground into fine powder (100 mg) and incubated into a 10 mL 0.5 M HNO3 solution subjected to shaking extraction for 48h at room temperature. Afterwards, we used centrifugation at 12,000 rpm for 10 min to settle the solid material down into the tube bottom, and then we transferred the extracts and diluted them with deionized H2O (Milli-Q, Merck KGaA, Darmstadt, Germany) to measure the Na+ or K+ content.
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10

Adsorption of Cadmium by Magnetic Graphene Oxide

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The Cd(II) stock solution (1000 mg/L) was prepared by dissolving 1.000 g pure cadmium powder in 20 mL HNO3 solution (20%) in a 1000 mL flask, with Milli-Q water added up to the mark. Working solutions were prepared by appropriate dilution of stock solution using Milli-Q water. All adsorption experiments were performed by adding MGO suspensions to achieve the required adsorbent concentration, and performed in a constant temperature shaker with a rotating speed of 180 rpm. The solution pH was adjusted using 0.01 mol/L NaOH or 0.01 mol/L HCl [27 (link)]. After 24 h of adsorption, MGO was separated from the solution with magnets. The Cd(II) concentration in the supernatant was measured using flame atomic adsorption spectrometry (PerkinElmer AA700, USA) [28 (link)]. All trials were in triplicate. The adsorption capacity (qe) of MGO was calculated by the following formula:
where C0 and Ce are the initial concentrations and equilibrium concentration of cadmium (mg/L), respectively. V is the volume of the suspension and m is the mass of MGO.
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