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710 icp oes

Manufactured by Agilent Technologies
Sourced in United States, Australia

The 710 ICP-OES is a high-performance inductively coupled plasma optical emission spectrometer designed for elemental analysis. It utilizes a plasma source to atomize and excite the sample, and an optical system to measure the specific wavelengths emitted by the elements in the sample. The 710 ICP-OES is capable of analyzing a wide range of elements in various matrices with high sensitivity and accuracy.

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13 protocols using 710 icp oes

1

Heavy Metal Analysis in Seaweed

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Seaweed samples were pulverized with zirconium oxide balls in a jar using a Retsch Vibration mill MM 2000 and divided into three replicates for each species. Next, approximately 100 mg for each sample was placed in open heat-resistant glass tubes (SCHOTT DURAN®, Rye Brook, NY, USA) and digested at 110 °C in a heating block using 69% HNO3 (ARISTAR®, Leicestershire, England for trace analysis) three times and the last time using 37% HCl (ARISTAR® for trace analysis). Lastly, the samples were dissolved in a 2% HCl solution (diluted with Milli-Q H2O). The concentrations of arsenic (As) and cadmium (Cd) were quantified via inductively coupled plasma-optical emission spectrometry (ICP-OES 710, Agilent Technologies, Amstelveen, The Netherlands).
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2

Heavy Metal Desorption and Quantification

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During harvest, roots were rinsed with distilled water and incubated for 30 min in an ice-cold desorbing solution of 5 mm PbNO3. Subsequently, roots were washed three times in distilled water and once in Millipore water. Leaves were rinsed three times with Millipore water. The fresh plant material was dried at 60 °C, weighed, and digested in 70–71 % HNO3 using a heat block. Element concentrations were measured via inductively coupled plasma-optical emission spectrometry (ICP-OES 710, Agilent Technologies, Australia).
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3

Leaf Cadmium Concentration Determination

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In order to determine leaf Cd concentrations, complete leaf rosettes were harvested and rinsed using distilled water. Subsequently, samples were oven-dried at 80°C and digested in HNO3 (70–71%) in a heat block. Cadmium concentrations in the leaf extracts were determined using inductively coupled plasma-optical emission spectrometry (ICP-OES 710, Agilent Technologies, Santa Clara, CA, USA).
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4

Mineral Analysis of Wheat Grains

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For all treatments, the kernels of plants in 9 pots (each replicate constituted 3 pots) were harvested at maturity, and after being air dried, the kernels were ground into whole wheat flour for the test of mineral components.
Samples were subjected to high-temperature digestion with an HNO3/HClO4 acid mixture (Johnson and Ulrich, 1959 ), and the mineral component (P, K, Ca, Fe, and Zn) contents were determined by inductively coupled plasma emission spectrometry (ICP−OES 710; Agilent Technologies, USA) (Tracy et al., 1991 (link)).
The accumulation of mineral components in wheat grains was calculated by multiplying the mineral component concentration by the grain weight. The wheat grain weight under different low-temperature treatments is shown in Supplementary Figure S1.
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5

Quantifying Elemental Composition in Plants

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Dry leaf material (0.1-0.5 g) was digested in 70-71 % HNO3 and dissolved in 2 % HCl.
After digestion, the clear colourless extract was brought to 25 mL volume with Milli-Q water.
Macronutrients (P, K, Mg, Ca, S) and micronutrients (Na, Fe, Cu, Zn, Mn) present in plant extracts were determined by inductively coupled plasmaoptical emission spectroscopy (ICP-OES 710, Agilent Technologies, Australia). Concentrations were calculated by the use of standard curves with known concentrations.
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6

Comprehensive Water Quality Analysis

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Key water quality parameters of the primary effluent were measured according to standard methods. COD was measured using a Hach DRB200 COD Reactor and Hach DR3900 spectrophotometer (program number 435 COD HR) following the US-EPA Standard Method 5220. Adequate dilutions and adjustments were made to minimise chloride interference during sample measurements. A Shimadzu analyzer (TOC-V CSH ) was used to determine TOC concentration. An inductively coupled plasma-optical emission spectroscopy (ICP-OES) system (ICP-OES 710, Agilent, Australia) was used to determine the sodium ion concentration in the samples. Temperature, pH, and electrical conductivity were measured using an Orion 4-Star pH/conductivity meter (Thermo Scientific, Waltham, MA).
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7

Plant Phosphorus Concentration Assays

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For the plant total P concentration assay, fresh plant samples were heated at 75°C until completely dry, and then ground into powder separately. Approximately 0.05 g of the plant dry samples were weighed and digested with H2SO4 and H2O2. After cooling, the digested samples were diluted to 100 ml with distilled water. Then, the concentration of P in the solution was determined with 710 ICP-OES (Agilent Technologies, Santa Clara, CA, United States). Each experiment was repeated three times.
For the soluble Pi concentration assay, Tissue Inorganic Phosphorus Content Detection Kit (Solarbio, Beijing, China) was used. Each sample consisted of five seedlings, which were ground into fine powder in liquid nitrogen, repeated three times.
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8

Trace Metal Content Analysis

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To analyze the trace metal content, samples were first digested in Piranha acid solution (3H 2 SO 4 : H 2 O 2 ) at 2 mg ml -1 . The sample was gently heated up to 80 °C to aid digestion and then to 290 °C to near-complete evaporation. The samples were then diluted in 10 mL of 1% HNO 3 solution and filtered through a 0.22 µm filter. Samples were analyzed for trace metals against a calibration standard using an Agilent 710 ICP-OES. Each metal was referenced using at least three optical emission wavelengths.
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9

Solubilization of Minerals in SY Medium

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For solubilisation experiments, a modified version of the methods described by Altomare et al. [7 (link)] was used. The minerals (20 mg) used in the present study were Ca3(PO4)2, Fe2O3, MnO2, CuO and metallic Zn which were added in powder form to 50 ml of sucrose-yeast extract (SY) medium separately. Three replicate flasks were sampled each day for 9 days to determine the pH values and soluble mineral contents in the culture medium. The mycelium was removed by filtration (0.45 μm), and the P, Fe, Mn, Cu and Zn contents in the filtrates were determined using an inductively coupled plasma optical emission spectrometer (710 ICP-OES, Agilent Technologies, California, USA). Uninoculated media in flasks that were processed in the same way were used as the control.
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10

Analytical Techniques for Plant Biomass

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Roots and leaves were harvested from 6-week-old plants, washed three times with tap water and rinsed twice (5 min each) with deionised water to remove any adhering nutrients. The leaves and roots were dried in a forced-air oven at 70 °C for ~48 h to a constant weight for dry weight measurements (Figs. 2b and 3b and Supplementary Fig. 4a). The dried samples were ground and passed through a 1.0-mm screen. Total N/C contents (Figs. 2g, h and 3g, h) were determined via the dry combustion method using an Element Analyser (vario EL, Elementar, Langenselbold, Germany). For the analysis of mineral elements, the dry biomass was digested in H2SO4 or HClO4. P concentrations were determined using the molybdate yellow method and K concentrations were determined by flame emission photometry (Supplementary Fig. 6)54 (link),55 (link). The other nutrient elements were measured by ICP (Agilent 710 ICP-OES). At least three plants per treatment were harvested, and three independent biological replicates were analysed for each treatment.
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