The removal experiment of heavy metal in mine wastewater was designed to test the potential of REEs/C for practical applications. Briefly, REEs/C (0.1 g) was placed in a 150 ml clear glass conical flask along with actual wastewater (50 ml) from a mine in Fujian Province. Then, it was shaken at 30 °C and 250 rpm to ensure sufficient reaction between REEs/Cs and lead nitrate solution. Finally, 1 mL was sampled at 0.5, 1, 4, 8, 12, 24, 48, and 72 h. The solution to be measured was obtained by filtration through a 0.22 μm filter, and was used to detect the concentration of each heavy metal ion using ICP-MS. Three replicates were set up for all treatments.
X series 2
The X Series 2 is a high-performance laboratory equipment designed for precise and reliable measurement. It features advanced sensor technology and intuitive controls for efficient data collection and analysis.
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482 protocols using «x series 2»
Removal of Pb(II) from Mine Wastewater using REEs/C
The removal experiment of heavy metal in mine wastewater was designed to test the potential of REEs/C for practical applications. Briefly, REEs/C (0.1 g) was placed in a 150 ml clear glass conical flask along with actual wastewater (50 ml) from a mine in Fujian Province. Then, it was shaken at 30 °C and 250 rpm to ensure sufficient reaction between REEs/Cs and lead nitrate solution. Finally, 1 mL was sampled at 0.5, 1, 4, 8, 12, 24, 48, and 72 h. The solution to be measured was obtained by filtration through a 0.22 μm filter, and was used to detect the concentration of each heavy metal ion using ICP-MS. Three replicates were set up for all treatments.
Fabrication of Zinc-Bioceramic Microneedles
Uranium Quantification in Plants via ICP-MS
The plant concentration factor (PCF) was calculated on dry weight basis as per [36 ,56 (link)]
where Cplant and Csoil represent the metal concentration in plant roots and soils on dry weight basis, respectively.
The plant transfer factor (TF) was also calculated on dry weight basis [56 (link)].
where Cshoot and Croot represent the heavy metal concentration in shoots and roots of plants on dry weight basis, respectively.
Lung Nanoparticle Retention Kinetics
In addition, particle retention was determined in exemplary organs, such as the liver and brain.
The retention half-times in lungs were calculated assuming a first order kinetics (m = m0 x e−kt). An exponential curve fit was processed based on the individual retention data at day 3, 45, 94 post-exposure (3 time-points; 6 animals each) in order to calculate the clearance coefficient and the half-time: k = ln2/t1/2 (Statistica™ software).
Toenail Trace Element Analysis Protocol
First, toenail (50–100 mg) samples were washed twice with 2 mL of a 5% (weight/volume) Triton water solution; secondly, they were washed twice using 2 mL of Milli-Q water; thirdly, they were washed twice using 2 mL of acetone; and fourthly, an additional ultrasound treatment (5 min) was conducted. After that, toenails were air-dried and digested with 800 µL of a (4:1) mixture of HNO3 and H2O2 of Ultra Trace Metals grade quality, in a Teflon reactor for microwave-assisted attack. Mineralisation was performed at 400 W, starting from room temperature, ramped up to 160 °C for 15 min, and held for 20 min at this temperature. Finally, the extracts were filtered through a 0.45 µm Polytetrafluoroethylene (PTFE) membrane filter before analysis.
The elemental content of 16 metal(loid)s (Al, As, Cd, Co, Cr, Cu, Fe, Mn, Mo, Ni, Pb, Se, Tl, U, V, and Zn) in toenails was determined by an inductively coupled plasma mass (ICP-MS) system, using an XSeries 2 (Thermo Fisher Scientific Inc., Waltham, MA, USA) spectrometer at the Environmental Bioanalytical Chemistry Unit of Huelva University (Huelva, Spain). Analyses were performed blindly from the case-control status. The measured concentration was adjusted by the equipment, taking into account the dilution factor and sample weight, according to the following formula:
The limit of detection for each measured element was obtained from the calibration curve [41 ].
To control the quality of analysis, the following operations were conducted: (a) 100 mg of human hair was used as reference material (NSC DC73347a) with the purpose of correcting the instrumental variability in each sample batch, with a mean accuracy of 90% maintained along the time ±5%; (b) the ICP-MS response was monitored over time by a measurement of metal(loid)s concentrations at a point on the calibration curve (2 ng mL−1) every 20 samples analysed, ensuring an adequate evaluation of the instrument’s response; (c) an instrumental drift correction was performed with the addition of 100 ng mL−1 rhodium, as an internal standard, to all of the samples and calibrants, of which those whose response differed ± 10% with respect to the internal standard were measured again; (d) an analysis was conducted every 5 samples of reagents blanks containing 5% (v/v) HNO3 (Suprapur quality), 1% (v/v) HCl, and Rh 100 ng mL−1 in Milli-Q water; (e) an analysis was conducted of duplicate samples every 2.5 h of the sequence; (f) a spiked sample analysis was conducted by spiking the reference materials with the analytes under study (50 ng mL−1). Finally, potential interferences from 98Mo, 205Tl, and 238U, regularly existing in nails, were removed by operating the ICP-MS system in helium collision mode (He flow: 4 mL min−1); the operative conditions of ICP-ORS-MS are shown in
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Arsenic(III) Adsorption Performance of Templated Membranes
where Qe is the amount of As(III) adsorbed by the unit mass of TeMs (mg/g), C0 is the feed concentration (mg/L), Ce is the concentration of As(III) in aliquots (mg/L), V is the volume of the solution (L), and m is the amount of silver loaded on the membrane used (g). In the case where the pristine template was tested, the weight of PDMAEMA-g-TeMs and Q-PDMAEMA-g-TeMs were used in m (g).
The effect of pH on As(III) adsorption was studied in the pH range of 3 to 9. Other parameters were kept constant (initial As(III) concentration: 50 ppm; adsorbent dose: 2 × 2 cm2; contact time: 300 min). The pH of the solution was adjusted dropwise with 1.0 N HCl(aq) and 1.0 N NaOH(aq). The pH was measured using a digital pH meter, HANNA HI2020-02 (HANNA Instruments, Smithfield, UT, USA). All experiments were performed in triplicate.
The charge on the adsorbent surface depending on the pH value was studied by determining the pHzpc value in the pH range from 3.0 to 9.0 according to the method described in ref. [54 ]: 10 mL of NaCl solution (0.01 M.) was brought to the desired pH value (pHi) by adding 0.1 M. of HCl or NaOH. After that, sample with the size of 2 cm × 2 cm was added to each flask and shaken on a shaker IKA KS 3000i (IKA, Konigswinter, Germany) for 12 h at room temperature and the final pH (pHf) of the filtrate was measured using HANNA HI2020-02 pH-meter (HANNA Instruments, Smithfield, Smithfield, UT, United States of America).
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