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Multi n c 2100s toc analyzer

Manufactured by Analytik Jena
Sourced in Germany

The Multi N/C 2100S TOC analyzer is a versatile laboratory instrument designed to measure the total organic carbon (TOC) content in a wide range of samples. It employs high-temperature combustion technology to determine the TOC levels accurately and efficiently.

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2 protocols using multi n c 2100s toc analyzer

1

Characterization of Synthesized Samples

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Information concerning the crystal structures of the synthesized samples was acquired by powder XRD (Bruker AXS D8 diffractometer) with Cu Kα radiation (λ = 1.5406 Å). Thermogravimetric analysis (TGA) was conducted under constant nitrogen flow on a TA thermal analyzer at a rate of 15 °C/min from 25 to 800 °C. The FTIR spectra were recorded using an Agilent FTIR spectrometer with KBr. The N2 adsorption–desorption isotherms were collected using a Quanta Chrome Nova surface area and pore size analyzer at − 196 °C. The specific surface area of the samples was calculated by the BET method, and the total pore volume was determined from the volume of N2 taken up by the samples at P/P0 = 0.95. Besides, the BJH method was used to calculate the pore size distribution of the samples using the desorption branch of the isotherm. The surface morphologies of the samples were scrutinized with E-SEM (Thermo Scientific Quattro S). The chemical compositions and mapping images of the samples were determined by EDX associated with the E-SEM instrument. The XPS spectra were recorded on a Thermo-Fisher Scientific spectrometer with monochromatic X-ray Al Kα radiation. The total organic carbon (TOC) was measured on Analytic Jena multi N/C 2100S TOC analyzer.
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2

Comprehensive Wastewater Analysis Methods

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COD was measured in accordance with Standard Methods (APHA, 1998) . Protein concentration was determined with Lowry et al. (1951) using a UV spectrophotometer (UV-1800, Shimadzu, Kyoto, Japan) against a blank at wavelength 750 nm. Bovine serum albumin was used as the standard. Carbohydrate concentration was determined with the sulfuric-phenol method (DuBois et al., 1956) against a blank at wavelength 495 nm. D-Glucose was used as the standard. Protein and carbohydrate concentrations were converted to equivalent COD concentration with factors of 1.5 and 1.07, respectively as described previously (Rittman and McCarty, 2001) . TOC was analyzed with a Multi N/C 2100S TOC analyzer (Analytik-Jena, Jena, Germany). Sludge pH was measured with a pH meter (3200P, Agilent, Santa Clara, CA, USA). Sludge DD was expressed as the extent of sludge solubilization. It was calculated as follows (Muller et al., 1998) :
where SCOD T is the soluble chemical oxygen demand (SCOD) of treated sample, SCOD NaOH is the SCOD of sample immersed in 1 mol/L NaOH (1:1, V/V) at 90°C for 10 min and SCOD 0 is the SCOD of the untreated sample.
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