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Autosampler series 3000

Manufactured by Agilent Technologies

The Autosampler Series 3000 is a precision instrument designed to automatically introduce samples into an analytical instrument, such as a chromatograph or spectrometer, for analysis. The core function of the Autosampler Series 3000 is to accurately and consistently deliver samples to the instrument, ensuring reliable and reproducible results.

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4 protocols using autosampler series 3000

1

Elemental Analysis of Juncus acutus

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Juncus acutus roots and leaves (n = 10 for every treatment) were washed with tap water (3×) followed by washing with distilled water in order to remove any adhered particles. Next, they were dried at 50°C for 4 days. Dried plant samples (0.2 g) were digested with 9 mL HNO3 (>69%, Sigma-Aldrich) and diluted with ultrapure water and centrifuged. Supernatants were subsequently filtered (0.45 μm, Whatman), diluted at 1:10 (v/v) with ultrapure water and analyzed by ICP-MS (ICP-MS 7500cx coupled with Autosampler Series 3000, both from Agilent Technologies).
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2

Contaminant Accumulation and Enzymatic Response

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Water samples were taken at days 0, 14, and 21 after addition of the contaminants and were analyzed for their concentrations of metals and organic contaminants. The soluble metals were determined by inductively coupled plasma mass spectrometry (7500cx coupled to Autosampler Series 3000, both from Agilent Technologies). BPA, CIP, and SMX concentrations were measured by high-performance liquid chromatography (HPLC) (Shimadzu Corp., Kyoto, Japan), equipped with LC-10 ADVP solvent delivery module, SPD-M10 AVP Diode Array Detector, RF-10AXL Fluorescence Detector, and SIL-10 ADVP autosampler. Separation of BPA was accomplished on a Nucleosil 100–5 C-18 column and separation of CIP and SMX was performed on an Alltech PrevailTM Organic Acid 5u as previously described by Christofilopoulos et al. (2016) (link).
At the end of the experiment, the plants were harvested and washed first with water and then with distilled water. The fresh weights of roots and leaves were determined, plant parts were cut in small pieces and 0.4 g of each plant compartment was sampled for enzymatic analysis while 0.3 g of roots was taken for DNA extraction. The plant samples for further analysis were immediately snap-frozen in liquid nitrogen and stored at -80°C; the remaining material was dried at 45°C and weighed.
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3

Aqueous Leachates Analysis by ICP-MS

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The aqueous leachates were produced by adding 0.2 g of the samples in 5 ml distilled water, dispersing with ultrasonic probe for 20 s, allowing standing for 1 h and subsequent centrifugation. The supernatant was stored in polyethylene bottles for ICP-MS analysis (7500CX coupled with Autosampler Series 3000, both by Agilent Technologies) for major and trace elements. The precision of the analyses was tested using elemental standards (1000mg/L) by Merck . The relative standard deviation of the analyses varied according to the concentration, typically 7% for the major elements, less for the trace elements.
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4

Characterization of Fe-oxyhydroxide Samples

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Two types of materials were analyzed: solid samples consisting principally of Fe-oxyhydroxides and aqueous solutions here referred to as “crudes” and “leachates” respectively. The latter were produced by adding 0.2 g of the crudes in 5 ml distilled water, dispersing with ultrasonic probe for 20 s, allowing standing for 1 h and subsequent centrifugation. The supernatant was stored in polyethylene bottles for ICP-MS analysis. In the case of the crudes, about 100 mg of each sample were digested in 10 ml concentrated HNO3, 2 ml concentrated HCl and 1 ml concentrated HF acids in teflon beakers on a hot plate with addition of 6 ml 0.625% EDTA at boiling point, following the EPA3051 method. The chemical composition of the samples and the leachates was determined by ICP-MS (7500CX coupled with Autosampler Series 3000, both by Agilent Technologies). The method is not suitable for determination of Si due to the use of HF in digestion and S due to analytical constraints. The precision of the analyses was tested using suitable standards. The relative standard deviation of the analyses varied according to the concentration, typically 7% for the major elements, less for the trace elements.
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