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12 protocols using ion chromatography

1

Tracking Nutrient Dynamics in Drainage Solutions

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The volume of drainage solution was measured each water sampling events and water consumption capacity (evaporated and uptaken by biota) was estimated as the difference between input and output volumes. Samples were further analyzed for dissolved inorganic and non-purgeable organic carbon (IC and NPOC), and total nitrogen (TN) by Shimadzu TOC-L system, and acidified and analyzed for same suite of elements as in plants by ICP-MS. Solution pH and conductivity were also measured each sampling time. Major anions, (bromide, sulphate, phosphate, fluoride and chloride) were analyzed by ion chromatography (Dionex). Additionally, pH and conductivity were measured by electronic pH and conductivity probes for each sample.
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2

Elemental Analysis of Leaf Nutrients

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The contents of free cations (K+, Na+, Ca2+, and Mg2+) and anions (NO3, Cl, SO42− and H2PO4) in leaves were determined with ion chromatography (DIONEX, Sunnyvale, CA, USA) [25 (link)].
The contents of total C and total N in L. chinensis leaves were measured with isotope mass spectrometer (Elementary various EL, Langenselbold, UK), and the content of total P was measured with molybdenum antimony resistance detecting method [26 ].
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3

Characterization of Manure Lagoon Sediments

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The near-bottom sediment slurry from the solid–liquid separation lagoon (site Tom1) was sampled on 12 July 2019. Manure slurry was sampled from the storage lagoon (site Tom3) on 18 October 2019. The pH, temperature, and redox potential measurements (Hanna Instruments, Vöhringen, Germany) were taken on-site by inserting the appropriate electrodes into the slurry. H2S concentrations in air were measured via an OKA-T portable gas analyser (Informanalitika, Russia) with electrochemical sensor (accuracy of ± 25% of reading). Anion concentrations in the pore water samples were measured using ion chromatography (Dionex). H2S was measured colourimetrically in triplicate with the methylene blue method37 (link) using a Smart Spec Plus spectrophotometer (Bio-Rad Laboratories, Hercules, CA). The elemental composition of the manure storage lagoon and solid–liquid separation lagoon was analysed by ICP-MS (Plasma Chemical-Analytical Centre, Tomsk). The mineralogical composition of the Tom1 sediment and Tom3 manure slurry were characterised by X-ray diffraction (XRD) using a Shimadzu XRD-6000 diffractometer as previously described38 (link). Air-dried sediment and slurry were examined under a Philips SEM 515 scanning electron microscope (SEM). Energy dispersive spectrometry (EDS) using an EDAX Inc. spectrometer (Mahwah, NJ) was performed at a voltage of 30 kV and a working distance of 12 mm.
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4

Sulfate Reduction Rates in Camel Feces

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Radioactive sulfate was used to determine the sulfate-reduction rates (SRR) in camel feces. Feces were placed in sterile 5 mL syringes sealed with butyl rubber stoppers, which received aliquots (300 µL) of Na235SO4 (3 µCi ‘Perkin-Elmer’, Waltham, MA, USA) by injection through the butyl rubber stopper. The syringes were incubated in the dark at 37 °C, for 24 h followed by the addition of 1 mL of 2M KOH to terminate the reaction and fix sulfide. Radioactivity was measured in the acid volatile sulfide (AVS), H2S and FeS, and chromium-reducible sulfur (CRS) fractions, which included pyrite, and elemental and organic sulfur, as previously described [25 (link),26 (link)]. Sulfate concentration was analyzed by ion chromatography (Dionex). The average SRR and standard deviation were calculated from triplicate incubations.
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5

Measuring Soil pH and Nitrates

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Medium pH was measured using a standard bench top pH meter. Nitrate concentrations were measured using ion chromatography (Dionex, Sunnyvale, CA), respectively, using previously described protocols [34 (link)].
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6

Elemental Analysis of Chemical Compounds

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The content of elements (C, H, N) was determined with a Yanaco CHN CORDER MT-6 Elemental Analyzer, and a Dionex Ion Chromatography was used to analyze the content of sulfur.
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7

Disproportionation of Sulfur Compounds

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The abilities of isolates to grow via the disproportionation of thiosulfate (10 mM), elemental sulfur (1% wt/vol), and sulfite (1, 5 mM) were tested with the MMJS medium in the absence or presence of Fe (III). All of the experiments were performed in duplicate. In addition, appropriate control experiments were performed in order to differentiate biotic and abiotic reactions. Serum bottles were homogenized via manual shaking, and aliquots of the cultures were sampled using a syringe that was nitrogen-flushed prior to sampling. The samples were processed immediately for further analyses in order to minimize oxygen exposure. Bacterial growth was measured via direct cell counts using a phase-contrast microscope (Eclipse 80i, Nikon). Before counting, the iron precipitates were dissolved using a dithionite solution (5% in 0.3 M acetic acid) (57 (link)). The dissolved sulfide concentration was determined spectrophotometrically using the methylene blue method, according to Cline (1969) (58 (link)). Thiosulfate and sulfate were analyzed via ion chromatography (Dionex, USA) after separation on an IonPac AG19 column (4 × 250 mm) with NaOH (20 mM) as the eluent at a flow rate of 1 mL/min. Fe (III) reduction was monitored by quantitatively measuring Fe (II) using the ferrozine method (59 (link)). The samples for the assay were prepared as described previously (60 (link)).
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8

Monosaccharide Analysis of Polysaccharide

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Ion chromatography (Thermo Fisher Scientific, USA) was applied to analyze the monosaccharide composition of RSP with 13 standard monosaccharides (fucose, rhamnose, arabinose, galactose, glucose, xylose, mannose, fructose, ribose, galacturonic acid, glucuronic acid, mannuronic acid and guluronic acid). Five mg of polysaccharide sample was accurately weighed, and 1 mL TFA acid (2.5 M) solution was added and heated at 121 °C for 2 h, followed by drying under nitrogen. Methanol was added to clean it and then dried under nitrogen. The methanol cleaning step was repeated 2–3 times. The sample was then dissolved in sterile water and transferred to the chromatographic flask for testing. An electrochemical detector was employed to detect the monosaccharide components. Mobile phase A was 0.1 M NaOH, and the mobile phase B was 0.1 M NaOH and 0.2 M NaAC. With 5 μL of injection volume, the samples were analyzed on a Dionex CarboPac PA10 column (250 × 4.0 mm, 10 um) at 30 °C with a flow rate of 0.5 mL min−1.
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9

Monosaccharide Composition Analysis of LBP

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The monosaccharide composition of LBP was determined by ion chromatography [58 (link)]. Then, 5 mg of LBP was precision weighed in ampoan ule bottle, 2 mL 3 mol/L trifluoroacetic acid as added, and the mixture was hydrolyzed at 120 °C for 3 h. The acid hydrolysis solution was transferred to the tube and dried by nitrogen blowing. Next, 5 mL of deionized water was added, dissolved and mixed. Then, 50 μL was added to 950 μL deionized water and centrifuged at 12,000 rpm for 5 min. The supernatant was analyzed by ion chromatography (Thermo Fisher, Shanghai, China). Chromatographic conditions: chromatographic column: Dionex CarbopacTM PA20 (3 × 150 mm); mobile phase: A: H2O; B: 15 mM NaOH:100 mM NaOAC (1:1); flow rate: 0.3 mL/min; sample size: 5 μL; column temperature: 30 °C; detector: Electrochemical detector.
The results were compared with 16 monosaccharide standards (fucose (Fuc), aminogalactose hydrochloride (GalN), rhamnose (Rha), arabinose (Ara), glucosamine hydrochloride (GlcN), galactose (Gal), glucose (Glu), xylose (Xyl), mannose (Man), fructose (Fru), ribose (Rib), galactose aldehyde acid (GalA), glucuronic acid (GlcA), N-acetyl-D-glucosamine (GlcNAc), guluronic acid (GulA), and mannose aldehyde acid (ManA)) to determine the monosaccharide species and molar ratio.
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10

Ion Chromatography Analysis of Sulfate and Phosphate

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Ion chromatography (Thermo Scientific, Germany) was utilized for the measurement of SO42− and PO43− ion concentrations in concentrated sulfuric acid, phosphoric acid, fresh MA, and recovered acid liquors after each reaction. After adjusting the concentration to the calibration range, 0.10 mL of the acids were diluted to 100 mL with distilled DI water and investigated for SO42− and PO43− ion concentrations. The results obtained with this machine are based on ppm units [51 ].
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