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Ethos plus

Manufactured by Milestone
Sourced in Italy

The Ethos Plus is a laboratory instrument designed for sample preparation and digestion. It provides controlled heating and agitation to facilitate the dissolution of solid samples in various acid or solvent media. The core function of the Ethos Plus is to prepare samples for subsequent analysis, such as elemental determination or compositional characterization.

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18 protocols using ethos plus

1

ICP-MS Analysis of Essential Ions in Plants

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For ICP‐MS analyses of Na+, K+ and Ca2+, roots and shoots were harvested from salt stressed plants including HM053 inoculated salt stressed plants. Tissues were dried in an oven, weighed and ground up by hand using a mortar and pestle. The samples were digested in 3.0 ml of concentrated nitric acid at 190°C using a Milestone Ethos Plus (Milestone SRL) microwave digestion system, then were diluted to 50 ml with ultrapure water followed by gravimetric dilution by a factor of 10 with 0.45 M nitric acid. Samples were analyzed via Perkin‐Elmer NexION ICP‐MS in Kinetic Energy Discrimination mode. Reference materials included NIST SRM 1570 spinach leaves and NIST SRM 1573 tomato leaves prepared as samples and analyzed in the same way. Internal standards at known concentrations were prepared from stock solutions (High Purity Standards) and used to calibrate instrument response.
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2

Quantifying Elemental Composition in Plants

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For ICP-MS analyses, roots and shoots were dried in an oven, weighed into digestion vessels and digested in 3.0 mL of concentrated nitric acid at 190 °C in a Milestone Ethos Plus (Milestone SRL, Sorisole, Italy) microwave digestion system. Digestants were diluted to 50 mL with ultrapure water and gravimetrically diluted by a factor of 10 with 0.45 N nitric acid. Samples were analyzed via Perkin-Elmer NexION ICP-MS in Kinetic Energy Discrimination mode. Total elemental ion counts were measured of 56Fe and normalized to 12C counts. Reference materials included NIST SRM 1570 spinach leaves and NIST SRM 1573 tomato leaves prepared as samples were. Internal Calibration standards of Sc, In, and Tl at known concentrations were used from stock solutions (High Purity Standards, Charleston, SC 29418, USA).
For Laser Ablation-ICP-MS, roots were removed from shoots and a 3-cm section of primary lateral root was further excised above the apical meristem. Roots were sectioned in OCT embedding media to 100 μm thickness (Fisher Scientific Inc., Hampton, NH 03801, USA) and placed on quartz microscope slides for freeze drying in a FreezeZone 1 dryer (Labconco Corp., Kansas City, MO, USA) before ablation.
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3

Soil and Plant Element Analysis

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To determine the “pseudo-total” element content of the soil, the Hungarian Standard MSZ 21470-50 2006 was followed with slight modifications. The sample preparation procedure and the microwave digestion of 0.5 g of soil (<0.1 mm) in cc. HNO3 and in cc. H2O2 (3:1 v v−1) solutions are described in detail elsewhere [87 (link),88 (link)].
To determine the soluble (“plant-available”) element content of the soil, the MSZ 20135 [93 ] was followed. The sample preparation procedure and the extraction of 0.5 g soil (<0.1 mm) with Lakanen–Erviö (LE) solution (0.02 M H4-EDTA in 0.5 M ammonium acetate buffer and 0.5 M acetic acid, pH 4.65; Lakanen and Erviö, 1971) is described in published articles [87 (link),88 (link)].
From the prepared (dried and ground to particles < 0.1 mm) plant samples, 0.5 g was loaded into the pressure-proof bombs of the microwave digester (Milestone Ethos Plus, Sorisole BG, Italy). To all samples, 5 mL of distilled cc. HNO3 and 3 mL 30% (v v−1) H2O2 (Scharlau, Barcelona, Spain) were added [87 (link)].
Elemental analysis of all soil or plant samples was conducted with the inductively coupled plasma optical emission spectrometry (ICP-OES) technique, applied on an iCAP 7000 spectrophotometer (Thermo Fischer Scientific, Waltham, MA, USA). For the calibration, a multielement standard solution (n = 2) was applied. All element analyses were performed with 4 replicates.
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4

Labneh Physicochemical Characterization

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Representative Labneh samples were sampled as indicated by AOAC (920.122, 955.30). Total solids, protein, fat in milk, fat in Labneh, ash, titratable acidity, and pH were determined by the AOAC 2005 official methods (926.08, 2001.14, 2000.18, 933.05, 935.42, and 920.124, respectively). Syneresis was determined as indicated by Al-Kadamany et al. (2003 ) but using Whatman No. 1 filter paper. Mineral analysis was performed by the acid digestion method according to the protocol mentioned for cheese ashes by the microwave Ethos Plus (Milestone Inc., Monroe, CT), June 2000.
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5

Micronutrient Analysis of Leaf Samples

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Leaves (fertilized and untreated controls) were washed thoroughly twice with ultrapure water Type I. Leaves were dried in an oven at 60°C, ground in a ZrO2 ball mill (MM301, Retsch, Haan, Germany) and stored at room temperature until analysis. Plant samples (200 mg DW of tissue) were digested using a microwave system (Milestone Ethos Plus, Bergamo, Italy) with 6.4 mL HNO3 (26%, TraceSelect Ultra, Sigma–Aldrich) and 1.6 mL H2O2 (30%). The microwave digestion program was 5 min at 100°C, 10 min at 170°C, and 35 min at 180°C. The digest was filtered through a 0.45 μm PTFE filter, diluted to 10 mL in water Type I, and metals (Fe, Mn, Cu, and Zn) determined by flame atomic absorption spectrometry (FAAS) using a Solaar 969 apparatus (Unicam Ltd, Cambridge, UK). Three replications per treatment and batch were analyzed. Total micronutrient contents in leaves were obtained from the leaf concentrations and DW values. Iron concentration data were analyzed using two-way ANOVA and means compared (Fisher’s LSD test at p < 0.05) using Genstat.
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6

Determination of Total Chromium in Soils

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The content of total chromium in both the natural and spiked soils was determined after wet mineralisation of soil in a mixture of HNO3:HF (5 mL:1 mL). Samples (0.2 g) were heated in closed Teflon vessels in a microwave digestion system (Ethos Plus, Milestone, Italy) according to optimised microwave program: 250 W for 2.5 min, 500 W for 5 min and 700 W for 15 min. The process was repeated twice for total digestion of soil. The obtained solutions were transferred into polyethylene vessels, diluted with Milli-Q water to the final volume of 15 mL and analysed by ETAAS. The chromium content in the mineral soil (M) was 16.9 μg g−1, while in the organic soil (O) it was 18.3 μg g−1. The average content of chromium in mineral soil spiked with different chromium compounds was 34.2 ± 5.1 μg g−1 (the average spiking efficiency was equal to 68%), while in the spiked organic soil it was 38.4 ± 4.5 μg g−1 (the average spiking efficiency was equal to 76%).
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7

Mineral Analysis via Microwave Digestion

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Samples were mixed with 3 mL water, 150 µL concentrated HCl and 750 µL HNO3 in Teflon vials followed by microwave digestion (Milestone microwave laboratory system Ethos Plus Sorisole, Italy) as described previously (Larsson et al., 2007, J. Agric. Food Chem. 2007, 55, 9027–9035 9027). Analysis of minerals was performed using atomic absorption spectroscopy on an Agilent Technologies 200 Series 240FS AA with an UltrAA Boosted Lamp Supply. Quantification was made using standard curves of iron, zinc, and copper standards (Fluka, Buchs, Switzerland).
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8

Comprehensive Analysis of Dried Fruit Pomace

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The samples of dried fruit pomace were analyzed for basic composition, level of minerals (calcium, magnesium, potassium), fatty acid profile, and anthocyan content (Table 2). All the analyses were performed in accordance with the methods described by Pieszka et al. (2015) .
Basic composition of dried pomaces was determined by standard methods (AOAC, 1995 ). Mineral content was determined by atomic absorption spectrometry (AAS) on ICP-MS spectrophotometer after previous mineralization in a microwave oven (Milestone Ethos Plus, Sorisole, Italy). The concentration of anthocyans was determined using a JASCO V-530 spectrophotometer (Jasco, Tokyo, Japan). The fatty acid profile of the pomace samples was determined using gas chromatography (Varian 3400, Woonsoket, RI).
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9

Arsenic Mineralization in Microwave-Assisted Digestion

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Mineralization of arsenic-loaded gBIOs after the sorption experiments was performed in 69% HNO3 and 30% H2O2, in a closed microwave system (Milestone Ethos Plus) at controlled thermal conditions (180°C) for 25 min. Total arsenic and zinc concentration in the samples were measured by atomic absorption spectrometry with an air-acetylene flame atomizer (TJA Solution, SOLAAR M, UK) (DL 1 μg/L). Arsenic and zinc standard solutions (Merck, Darmstadt, Germany) were prepared in 3% HNO3.
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10

Micronutrient Analysis of Potato Tubers

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For laboratory studies, 50 different-sized tubers (with diameters of 30–60 mm) were taken from 10 successive randomized plants per plot. Tuber sections cut out along the longitudinal axis from the tuber tip to the stolon attachment site were crumbled and 2-stage dried at an initial temperature of 60 °C, and then, at 105 °C to determine the tuber dry matter with the gravimetric method [64 ]. The contents of Fe, Zn, Cu, B, Mn, and Si were determined with the inductively coupled plasma optical emission spectrometry (ICP-OES) method (Optima 8300, Perkin Elmer, Waltham, MA, USA) after sample mineralization in a mixture of concentrated HNO3 and 20% H2O2 (3:1) in a microwave system (Ethos Plus, Milestone, Sorisole, Italy) [65 ]. All assays were performed in duplicate, and the mean contents of micronutrients were expressed as milligrams per kilogram of potato tuber dry matter (DM) ± standard deviation (SD).
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