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Dionex dx 600

Manufactured by Thermo Fisher Scientific
Sourced in United States

The Dionex DX-600 is an ion chromatography system designed for the analysis of ions and ionic compounds. It is capable of performing both anion and cation analysis. The system includes a high-pressure pump, an automated sample injection system, and a conductivity detector. It is suitable for a wide range of applications in various industries, including environmental, pharmaceutical, and food analysis.

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5 protocols using dionex dx 600

1

Peat Slurry Methanogenesis Inhibition Assay

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In the laboratory, slurries from each site were prepared using previously established procedures (Duddleston et al., 2002 (link); Zhang et al., 2020 (link)) in a glove bag filled with 100% N2 gas. Excess pore water was squeezed from the peat and woody plant roots and any remaining green vegetation were removed. About 100–300 g peat (wet weight) was homogenized with pore water in a blender at a ratio of ∼1:3 wet weight peat: total volume slurry. Slurries prepared in this manner contained 0.04–0.08 g dried peat per mL. In each of the 200 mL serum bottles, 50 mL of slurries were mixed with 100 mL MilliQ water and incubated for 50 days. On day 1, one set of serum bottle (n = 2) per treatment was amended with 1 mL of 500 mM BES to inhibit methanogenesis (Compeau and Bartha, 1985 (link)). Slurry samples (1.0 mL) for anion analysis were periodically collected from incubation bottles using a plastic 1.0 mL syringe. Samples were centrifuged (12,000 × g) for 5 min and the supernatant filtered through a 0.22 μm sterilized PES syringe filter (Celltreat). Anions (acetate, propionate, butyrate, SO42–, and NO3) were measured by injecting 25 μL of filtered supernatant into an automated Dionex DX600 ion chromatograph (Thermo Scientific) fitted with an AS11HC ion exchange column (4 mm) with suppression and with a potassium hydroxide gradient eluent generator and conductivity detector.
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2

Purification and Characterization of 4-MDDT

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4-MDDT was purified at room temperature using a Dionex DX-600 HPLC system (Thermo Scientific, Hemel Hempstead, UK), Prevail Select C18 5 μ (250 mm × 4.6 mm i.d.) HPLC column. Elution at a flow of 1 ml/min was performed with a linear gradient between solvent A (50% methanol : 0.1% trifluoroacetic acid v/v) and solvent B (98% methanol : 0.1% trifluoroacetic acid v/v). Peak identification was performed by comparing spectra (collected between 220 and 500 nm). Fractions were collected, dried down under nitrogen stream and 4-MDDT resuspended in DMSO at 50 mM using its molecular mass as 413, as measured by GC-MS analysis (see below).
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3

Characterization of PM2.5 Chemical Composition

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Subsamples of PM2.5 filters were taken for analyses of heavy metals, water-soluble ions and organic carbon contents. For water-soluble components, filter pieces immersed in ultrapure water were sonicated for 1.5 h in a pre-cooled ultrasonic cleaner, and then the PM2.5 suspension was filtered by 0.22 μm filtration membranes.
The major anions (Cl -, NO3 -and SO4 2-) were determined by Dionex ICS-1100 (Thermo Fisher Scientific, USA), the major cations (Na + , K + , NH4 + , Ca 2+ , and Mg 2+ ) were analyzed by Dionex DX-600 (Thermo Fisher Scientific, USA), and the water-soluble organic carbon (WSOC) was determined by TOC-V-CPH/CPN. For the contents of metal, filter samples were digested by HNO3-HClO4-HF acids, and determined by inductively coupled plasma-optical emission spectrometer (ICP-OES, Optima8000, PerkinElmer) and ICP mass spectrometer (ICP-MS, NexION300X, PerkinElmer).
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4

Metagenomic Analysis of Diverse Hot Spring Sediments

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The sampling expedition took place in August 2019. Surface sediment samples were collected from the Quzhuomu hot spring (QZM1; 28°24.4′ N, 91°81.1′ E), downstream of Daggyai hot spring (DG2; 29°59.9′ N, 85°75.1′ E), and Xiaochaidan Lake (XCDL20; 37°27.3′ N, 95°28.5′ E), China (see Fig. S1 in the supplemental material). These sediments were collected into 50-ml sterile centrifuge tubes and were stored immediately on dry ice until arrival in the laboratory. Physicochemical parameters were measured either in situ or in the laboratory, as previously described (71 (link)) and listed in Data Set S1a. In brief, the pH, temperature (T), and concentration of dissolved oxygen (DO), Fe2+, and S2− were measured in situ with a temperature/pH probe (DR850; HACH Company, CO) and Hach kits, respectively. Total organic carbon (TOC) and dissolved organic carbon (DOC) were measured with a Multi N/C 2100S analyzer (Analytik, Jena, Germany). The concentrations of major ions (e.g., K+, Ca2+, Na+, Mg2+, Cl, and SO42−) were determined by using a Dionex DX 600 ion chromatograph (Dionex, USA). Genomic DNA was extracted from 10 g of each sediment sample using our modified phenol-chloroform method (72 (link)). Standard shotgun libraries of 300 bp in insert size were conducted at the Guangdong Magigene Company and then were sequenced on an Illumina HiSeq 4000 platform (paired-end 150-bp mode).
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5

Characterization of Water Sources for Irrigation

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Two types of water sources were used: i) secondary effluents from the urban wastewater (UWW) treatment plant of El Bobar (Almería, Spain). This secondary effluent was directly used as positive control for irrigation assays and also it was solar treated (as described below) and used for irrigation assays; and ii) commercial mineral water (Aguas del Marquesado S.L., Spain) was used as negative control in the irrigation experiments.
Chemical characterization of UWW and mineral water is shown in Table S1 (Supplementary information). Total Organic Carbon (TOC) was analysed using a Shimadzu TOC-5050 (Shimadzu, Japan). Ionic concentrations was measured with a Dionex DX-600 (Dionex, USA) IC system for anions, and with a Dionex DX-120 system for cations. Turbidity was determined using a turbidity-meter (Model 2100 N Hach, USA) and conductivity with a conductivity sensor (GLP31, CRISON, Spain).
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