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Toc analyzer

Manufactured by Elementar
Sourced in Germany

The TOC (Total Organic Carbon) Analyzer is a laboratory instrument designed to measure the total organic carbon content in a sample. It provides an analysis of the organic carbon present in liquids, solids, or gases. The TOC Analyzer uses a combustion or oxidation process to convert the organic carbon compounds into carbon dioxide, which is then detected and quantified.

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5 protocols using toc analyzer

1

Spectroscopic and Chromatographic Analysis of Organic Pollutants

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The residual concentration of OG and RhB in the reaction system were detected using UV spectrophotometer, at detection wavelengths 475 nm and 554 nm, respectively. The residual concentrations of ACT, STZ and BPA were determined form high performance liquid chromatography (LC-20A, Shimadzu, Japan) with a photodiode array detector (SPDM20A). A Zorbax SB-C18 column (4.6 × 250 mm, 5 μm) (Agilent, USA) was used at a column temperature of 30 °C. A mixture of methanol (A)/0.3% formic acid solution (B) (30 : 70, v/v, for ACT and STZ; 70 : 30, v/v, for BPA) was used as the mobile phase at a flow rate of 1.0 mL min−1. Total organic carbon (TOC) was determined using a TOC analyzer (Elementar, Germany). The degradation products were detected using a 7890B/5977C GC-MS (Agilent, USA). The reactive oxide species (ROS) generated form the system was detected using an EPR spectrometer (Bruker A320, USA).
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2

HPLC-QTOF/MS Analysis of DCF Degradation

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The concentration of DCF was determined by a high-performance liquid chromatograph (HPLC, Waters 2695) equipped with a C18 column (4.6 × 150 mm, 5 μm). The column temperature was 30 °C with the injection volume of 20 μL. The mobile phase consisted of 0.1% acetic acid aqueous solution and methanol (25 : 75, v/v) at a flow rate of 1 mL min−1 and the detection wavelength was set at 276 nm. DCF degradation products were detected by an ultra-high performance liquid chromatograph-quadrupole time-of-flight tandem mass spectrometer (UPLC-QTOF/MS). The C18 column (2.1 × 100 mm, 1.7 μm) was used as a stationary phase with the column temperature of 30 °C. The mobile phase was a mixture of 0.1% formic acid water solution (A) and acetonitrile (B) at a flow rate of 0.3 mL min−1. The gradient elution procedure was 90% A for 1 min constantly, linearly decreasing to 0% A (100% B) for 12 min, keeping for 3 min and slowly increasing to 90% A for 18 min. The injection volume was 10 μL. The electrospray ionization (ESI) was used in the mass spectrometer to scan in the positive ion mode, and the scan range was m/z 50–500. All the mass spectrum data were analyzed by Masslynx 4.1 software. The mineralization of DCF was assessed through measuring the total organic carbon (TOC) of the reaction solution using a TOC analyzer (Elementar). The solution pH was monitored by a pH meter (PHS-3C, Leici).
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3

Quantifying Environmental Nutrients and Metals

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Ammonia nitrogen (NH4+-N), nitrite nitrogen (NO2-N), and nitrate nitrogen (NO3-N) were extracted with 2 mol/L KCl solution for 1 h and then measured colorimetrically by a spectrophotometer (Shimadzu, Japan; Long et al., 2017 (link); Xu et al., 2017a (link)). Dissolved organic carbon (DOC) was extracted by ultra-pure water and quantified using a TOC analyzer (Elementar, Germany). Metals (Cd, Cr, Cu, Mn, Ni, and Zn) were firstly digested by combined acids (HNO3-HClO4-HF) and then determined by the ICP-OES (PerkinElmer, United States; Xu et al., 2017b (link)). The pH was measured by a pH meter (Mettler Toledo, Switzerland) with a solid to ultra-pure water ratio of 1:2.5 (Shi et al., 2021 (link)). The physicochemical attributes were listed in Supplementary Table S2.
The distance-based (Bray-Curtis distance) redundancy analysis (db-RDA) and Mantel test were carried out to reveal the relationships between DAMO bacterial communities and environmental factors. The db-RDA and Mantel test were conducted using “vegan” package (version 2.6-2) and “linkET” package (version 0.0.3.3) in the R software (version 4.0.2), respectively.
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4

Soil Organic Carbon and Microbial Biomass Quantification

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SOC was measured by dichromate oxidation23 (link). Carbon (C) from the microbial biomass was extracted using the chloroform fumigation and extraction method24 (link). For this, 12.5 g of soil (fresh weight basis) were subjected to 48-h fumigation with chloroform in a glass desiccator. Triplicate subsamples of fumigated and non-fumigated soils from each of the three field soil samples were shaken for 30 min at 200 strokes per minute with 0.5 M K2SO4 at a ratio of 5:1 (extractant to fresh soil weight) and filtered through medium-speed quantitative filter paper, then placed at −15 °C until measurements. Organic carbon concentration in the filtrate was measured by a Shimadzu TOC-5000A analyzer (Shimadzu Corp., Kyoto, Japan). MBC was calculated as the difference between fumigated and non-fumigated samples. DOC concentration in soil samples was determined by a TOC analyzer (Elementar Analysensysteme GmbH, Germany)25 (link).
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5

Characterizing Pepper Plant Growth and Soil

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Various parameters of each pepper, such as shoot length, shoot diameter, shoot dry weight, root dry weight and leaf area were measured during the vegetative period. Parameters of fruit quality, including concentrations of vitamin C (VC), soluble sugars, proteins and nitrate were determined. Soil physical and chemical properties were analyzed. Soil available phosphorus (AP) was extracted with 0.5 M NaHCO3 and then determined using the ammonium molybdate ascorbic method. Soil organic C (SOC) and total N (TN) were determined using a TOC analyzer (Elementar, Langenselbold, Germany). Soil pH was assayed in a soil extraction solution (1:2.5, w/v) with a compound electrode (PE-10; Sartorious, Göttingen, Germany). Available potassium (AK) was extracted with 1 M ammonium acetate solution and then determined using a flame spectrophotometer (FP640: INASA, Shanghai, China). NO3-N and NH4+-N were extracted with 0.01 M CaCl2 and the contents were determined with a continuous flow analytic system (Santt System; Skalar, Holland).
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