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18 protocols using unicube

1

Soil Nutrient Analysis Methods

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Soil samples were collected from the central square of each plot (dimensions 2 × 2.5 m2). In each plot, 5 soil cores weighing about 400 g were collected from the root zone of 5 plants at a depth of 0–20 cm. Samples were prepared according to Miller et al. [58 ] and analyzed to determine the total N, NO3-N, NH4-N, and plant-available P and K concentrations. Total N in soil samples was determined by high temperature combustion using an elemental analyzer (Unicube, Elementar Analysensysteme GmbH, Hanau, Germany). To determine the concentration of mineral N (N-min, i.e., NO3-N + NH4-N) in the soil, each sample of sieved soil was extracted using a KCl solution, as described by Keeney and Nelson [59 ]. Subsequently, the NO3 and NH4 concentrations in the sample extracts were determined by applying the cadmium reduction to NO2 and the indophenol blue methods, respectively [59 ], using a Spectronic Helios spectrophotometer (Thermo Electron Corporation, Mercers Row, Cambridge CB5 8HY, UK). Plant-available P was determined using the Olsen method [60 ] and quantified by molybdate colorimetry [61 (link)]. Exchangeable soil K was determined using a flame photometer (Sherwood Model 420, Sherwood Scientific, Cambridge, UK) following extraction with an ammonium acetate solution.
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2

Characterization of Aloe vera Powder and Its Interaction with Food Components

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De Man, Rogosa, and Sharpe (MRS) media was purchased from BD Biosciences (Franklin Lakes, NJ, USA). A. vera powder was obtained from Morinaga Milk Industry Co. (Tokyo, Japan). ⍺-amylase, pepsin, and bile salt were purchased from Fujifilm Wako Pure Chemical Corporation (Osaka, Japan), and pancreatin was obtained from Sigma (St. Louis, MO, USA). A commercial soft drink and milk (pasteurised) were purchased from a local market. All chemical reagents used in this study were of analytical grade.
Data were collected using a muffle furnace (MFP-300A; IKEDA Scientific Co., Tokyo, Japan), an organic elemental analyser (UNICUBE; Elementar Analysensysteme GmbH Langenselbold, Germany), a scanning electron microscope (JSM-6330F; Tokyo, Japan ), a FT-IR spectrometer (FT-IR 300; JASCO, Tokyo, Japan), a zeta potential instrument (Melles Griot, Carlsbad, CA, USA), an Isoton II diluent instrument with particle size data analyser (Muiltisizer 4, Beckman Coulter, Brea, CA, USA), a high-performance liquid chromatograph (LC-10AS, Shimadzu, Kyoto, Japan), a gas chromatograph (GC-4000, TC-1; GL Sciences, Tokyo, Japan), and a colour measuring instrument (Konica Minolta, Tokyo, Japan).
Samples were prepared using a lyophiliser (Eyela, Tokyo, Japan) and spray drier (pilot-scale SD 1000; Eyela) for further analysis. Double distilled water was used in all experiments.
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3

Spectroscopic Analysis of Organic Compounds

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Starting materials and reagents were purchased from Sigma-Aldrich (Thermo Fisher Scientific, Waltham, MA, USA). The following instruments were used: IR spectra, Perkin-Elmer Spectrum One FT-IR spectrophotometer with ATR sampling unit; nuclear magnetic resonance spectra, BRUKER Avance 300 spectrometer; chemical shifts are given in parts per million (δ) downfield from tetramethylsilane as internal standard; mass spectra, Varian MAT 311A (EI); Thermo Fischer Scientific Q Exactive (ESI-HRMS); Elementar Unicube (EA).
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4

Determination of Nutrient Contents and Efficiencies

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Total carbon (C) and nitrogen (N) contents were determined by dry combustion (UNICUBE, Elementar Analysensysteme GmbH, Langensenbold, Germany). The P concentration in root and shoot tissues was determined colorimetrically on dry plant material (50 mg) after sulfuric‐perchloric digestion using the malachite green method (Ohno & Zibilske, 1991 ). Phosphorus‐acquisition efficiency was calculated as the ratio of P accumulated in tissues to exogenously supplied P during both plant growth in sand and the hydroponic experiment, while P‐utilization efficiency was calculated as the ratio of dry biomass to P content in plant tissues (Neto, Favarin, Hammond, Tezotto, & Couto, 2016 (link)). Root‐to‐shoot P translocation was indirectly estimated calculating the ratio of P content in the shoot divided by P content in the root.
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5

Comprehensive Material Characterization Protocol

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The crystal structure was analyzed by X-ray diffraction (XRD, SmartLab, Rigaku) analysis, using Cu Kα radiation (λ = 1.54,059 Å) at 40 kV and 30 mA over a 2θ range from 20 to 90° at a scan rate of 4 ° min−1. X-ray photoelectron spectroscopy (XPS, NEXSA, Thermo Scientific) with a monochromatic Al Kα source was also employed to confirm the molecular structure. The carbon 1s spectrum at ∼284.99 eV was used as a reference for calibration. Raman spectroscopy (LabRAM, Horiba) was performed to check the carbon structure. Field-emission scanning electron microscopy (FE-SEM, Crossbeam 540, Carl Zeiss) coupled with energy-dispersive X-ray spectroscopy (EDS) were employed to investigate morphology and distribution of the sample composition, while transmission electron microscopy (TEM, JEM-1400 Plus, JEOL) was utilized to confirm its microstructure. CHNS analysis (CHNS-O, UNICUBE, Elementar) was used to determine the carbon content.
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6

Oxygenation of Pentafluorophenyl Ketimine

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All reactions were conducted under argon atmosphere using standard Schlenk and glovebox techniques (<0.1 ppm O2, <0.1 ppm H2O). Toluene, benzene, n-hexane and n-pentane were degassed with nitrogen, dried over activated aluminium oxide (MBraun SPS) and stored over 3 Å molecular sieves. Deuterated solvents were dried over Na/K alloy and distilled under argon atmosphere, and a solution of tert-butylmagnesium chloride in Et2O (Sigma-Aldrich) was used as receive. 2-[(2,3,4,5,6-Pentafluorophenyl)amino]-4[(2,3,4,5,6-pentafluorophenyl)imino]-pent-2-ene (f5BDI-H) was synthesized according to the literature procedure57 (link). The oxygenation reactions were carried out using pure dioxygen dried by passing it through a tube filled with anhydrous NaOH/KOH. NMR spectra were acquired on Varian Inova 500 MHz and Varian Mercury 400 MHz spectrometer at 298 K. Elemental analysis were performed using an UNICUBE (Elementar Analysensysteme GmbH).
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7

Quantifying Organic Carbon in Minerals

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To verify the absence of organic carbon in the minerals, carbon content in minerals was determined (CHNS analyzer Unicube, Elementar Analysensysteme GmbH, Langenselbold, Germany). For samples with total carbon (TC) content above 0.1%, total inorganic carbon (TIC) was derived from carbonate analysis according to Scheibler (DIN EN ISO 10693 2014 ), and potential total organic carbon (TOC) content was calculated as difference from TC and TIC, which was relevant for SHCa-1 with 0.34% TOC.
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8

Comprehensive Catalyst Characterization

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The morphology of the catalysts was monitored by transmission electron microscope (TEM, FEI Tecnai G2 F20 S-Twin) with an accelerating voltage of 200 kV as well as the field-emission scanning electron microscope (FE-SEM, JEORJSM-6700F). The HAADF-STEM images were measured by JEOL JEM-ARM200F, which worked at an accelerating voltage of 300 kV. The atomic structure of the Co-S1N3 and reference catalysts was characterized using a JEOL ARM-200CF transmission electron microscope operated at 200 keV and equipped with double spherical aberration (Cs) correctors. The crystal phases were characterized by powder X-ray diffraction (XRD, Rigaku D/max 2500Pc, Cu-Kα radiation, λ = 1.5406 Å). The X-ray photoelectron spectroscopy (XPS) measurements were performed with a Perkin Elmer Physics PHI 5300 spectrometer using Al Kα nonmonochromatic radiation. The N2 adsorption/desorption curves were tested at 77 K using a Micromeritics ASAP 2020 surface area analyzer. The metal content was monitored by inductively coupled plasma optical emission spectrometry (ICP-OES), which was carried out on Thermo Fisher IRIS Intrepid II. The light elements (C, H, N, and S) contents of the Co-SxN4−x SACs were measured by an elemental analyzer (Elementar UNICUBE).
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9

Comprehensive Water Quality Analysis

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Turbidity was measured using a portable turbidity meter (2100Q; Hach Company, Loveland, CO, USA) and expressed in nephelometric turbidity units (NTUs). Oxidation reduction potential, dissolved oxygen, ammoniacal nitrogen, permanganate index, total phosphorus, and total nitrogen were measured by Zhejiang Hangbang Testing Technology Co., Ltd. pH was analyzed using a PB-10 pH meter (Sartorius, Göttingen, Germany). The C/N ratio was calculated based on carbon and nitrogen content in the sample determined by a micro elemental analyzer (UNICUBE, Elementar, Langenselbold, Germany). The metal concentrations were detected via inductively coupled plasma mass spectrometry (NexION-1000G; PerkinElmer, Waltham, MA, USA).
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10

Characterization of Sludge Biochar Properties

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The pH of sludge biochar was determined with reference to the “Determination of pH value of charcoal activated carbon test method” (GB/T12496.7-1999). The contents of C and H were analyzed using an organic elemental analyzer (UNICUBE, Elementar, Frankfurt, Germany), while the Si, Fe, and Al levels were determined through an Inductively Coupled Plasma Emission Spectrometer (ICP-OES) (Avio 200, PerkinElmer, Waltham, MA, USA). Furthermore, the specific surface area of the biochar was examined using a fully automated specific surface and porosity analyzer (ASAP 2460, Micromeritics, Atlanta, GA, USA). The microscopic morphology was visualized by scanning electron microscopy (SEM) (FEI Scios 2 HiVac, Thermo, Waltham, MA, USA). The physical phase composition and functional group structure were analyzed by X-ray diffractometer (XPS) (Smartlab 9KW, Rigaku, Akishima-shi, Japan) and Fourier transform infrared microscopy (FTIR) (Spotlight 200i, PerkinElmer, Llantrisant, UK), respectively.
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