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Pt 21

Manufactured by Sartorius
Sourced in China

The PT-21 is a laboratory equipment product. It is designed to perform a core function within the laboratory setting.

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4 protocols using pt 21

1

Soil Chemical and Physical Analysis Methods

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The SOC was measured by the Tinsley method (heated dichromate/ titration method). The total-N was determined by the Semimicro-Kjeldahl method. The amount of alkaline-hydrolyzable N (AN) was determined by the alkaline hydrolyzed diffusion method. Total P and K amounts were measured by the NaOH melt method. The available P (AP) was extracted with 0.05 N HCl–0.025 N H2SO4 solution and reacted with a solution of l-ascorbic acid and H2SO4–(NH4)6Mo7O24 methods. The available K (AK) was determined using flame photometry. All the above-mentioned methods were adapted from Bao71 and Wang, et al.50 (link).
The pH of soil solution (1 g soil in 5 mL deionized water) was measured using a pH-meter (Sartorius PT-21; Shanghai, China). The same soil solution was used for determining soil EC using an EC meter (DDS-307; Shanghai Precision Scientific Instruments Co., Ltd., China). Both pH and EC measurement were determined at the same time. Soil gravimetric water was calculated as follows: [(Fresh weight − Air-dried weight) / Dry weight] × 100%. Soil bulk density was calculated as follows: Air-dried soil mass/soil volume of 400 cm350 (link).
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2

Comprehensive Sediment Characterization

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The total nitrogen and carbon contents of the sediment were examined using the Vario Max CNS elemental analyzer (Elementar Analysensysteme GmbH, Hanau, Germany). The pH was determined using a pH meter (Sartorius PT-21, Shanghai, China) and a soil-to-ddH2O ratio of 1:2.5. Using a flow injection autoanalyzer, nitrate ( NO3- -N) and ammonium ( NH4+ -N) levels in sediment and water samples were determined (Westco Module 200, Smart Chem, France). Using an auto analyzer, the total phosphorus in sediment and water samples were also analyzed (AA3, Norderstedt, Germany). To evaluate the sediment moisture, 15 g of recent sediment was dehydrated in a 105 °C oven for 48 h. A TOC analyzer analyzed the total soluble organic carbon (TOC) in water samples (vario TOC cube, Elementar, Germany).
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3

Soil Carbon and Nutrient Storage Estimation

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Sample preparation details and some of the soil parameters analysis (e.g., bulk density, soil moisture, SOC, total N, available N, total K, available K, total P, available P, and soil texture) have been described previously by Wu et al. (2018 (link)). Soil porosity was calculated by the following formula: soil porosity = (1−bulk density/specific gravity) × 100%. The pH of the soil solution (one-part soil to five-parts water) was measured with an acidity meter (Sartorius PT-21, Shanghai, China). Soil electrical conductivity (EC) was determined with an EC meter (DDS-307, Shanghai Precision Scientific Instruments Co., Ltd., Shanghai, China) (Bao, 2000 ). Soil carbon or nutrient storage were computed as:
Farmland soil carbon or nutrient storage = αf × ρf × 0.2 × (1–Vgravel)
Poplar soil carbon or nutrient storage = αp × ρp × 0.2 × ρfp × (1–Vgravel)
where, αf and αp are the concentrations of farmland and poplar SOC (g kg−1); ρf and ρp are farmland and poplar soil bulk densities (Mg m−3), respectively; 0.2 is the soil thickness (0.2 m); and Vgravel is the proportion of gravel. Details regarding the bulk density correction can be found in Wuest (2009 (link)) and Wu et al. (2018 (link)).
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4

Comprehensive Soil Analysis Methods

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A Vario Max CNS elemental analyzer (Elementar Analysensysteme GmbH, Hanau, Germany) was used to determine the total carbon (TC) and nitrogen (TN) contents in the soil. NO3 and NH4+ were determined using a Discrete Auto Analyzer (SmartChem 200, WestCo Scientific Instruments Inc., Rome, Italy). Soil pH was measured using a pH meter (Sartorius PT-21, Shanghai, China) with 1:2.5 soil-to-ddH2O ratios. Fresh soil (15 g) was dried at 105°C for 48 h to measure soil moisture as drying-associated weight loss. Available potassium (AK), available calcium (ACa), available magnesium (AMg), available sodium (ANa), available copper (ACu), available iron (AFe), available manganese (AMn), and available zinc (AZn) were determined using an inductively coupled plasma emission spectrometer (ICP-MS) (Agilent, Santa Clara, CA, USA; 5100 ICP-OES). The Mo-Sb colorimetry method was used to determine the available phosphorus (AP) after the soil samples were extracted using NaHCO3 (0.5 M) (Bao, 2000 ). High performance liquid chromatography (HPLC) (e2695; Waters, Milford, MA, USA) was used to determine the glyphosate content.
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