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63 protocols using aanalyst 600

1

Quantification of Cd and As Bioavailability

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Before plant exposition, the bioavailable fraction of Cd and As was quantify in control and contaminated soils following the protocol of Lindsay and Norwell [13] . Briefly, 5 g of soil were extracted with 10 ml of 5 mM DTPA (Sigma-Aldrich), 0.1 M trietanolamine (Sigma-Aldrich) and 0.01 M CaCl2 (Sigma-Aldrich), for 2 h at 20°C under stirring. Samples were then filtered and metal concentrations were determined by graphite furnace atomic absorption spectroscopy (GFAAS; AAnalyst600, Perkin-Elmer). Nine soil samples for each treatment were processed.
Cd and As were also quantified in plant organs applying the USEPA 3051a protocol. The harvested plants were carefully washed with tap water and then with distilled water to remove soil debries before analysis. All the samples were dried at 100 °C overnight. For each sample 10 mL of HNO3 and 2 mL of HClO3 were added to 0.2 g of dry plant matter. The samples were digested by using the ETHOS HPR 100/10 microwave lab station (FKV, Bergamo, Italy) reaching the 180°C temperature. After their complete mineralization, they were opportunely diluted and analysed by graphite furnace atomic absorption spectroscopy (GFAAS; AAnalyst600, Perkin-Elmer). Standards (from ENEA Research Centre, Roma, Italy) and blanks were run with all sample series for quality control.
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2

Water Sampling and Arsenic Analysis

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Water sample collection, sample handling, and analysis for this study were performed as previously described (Chervona et al., 2012 (link)). The water As samples were analyzed at Columbia University’s Lamont Doherty Earth Observatory by inductively coupled mass spectrometry (ICP-MS), with a detection limit of 0.1 µg/L. Total urinary As (uAs) concentrations were measured at Columbia University Trace Metals Core Lab by GFAA spectrometry using an AAnalyst 600 graphite furnace system (PerkinElmer), as described (Nixon et al., 1991 (link)). This laboratory is part of a quality control program run by the Institut de Sante Publique du Quebec, Canada. Intraclass correlation coefficients (ICCs) were 0.99 between the Columbia laboratory’s values and samples calibrated at the Quebec laboratory. To correct for hydration status, urinary creatinine was analyzed using a method based on the Jaffe reaction.
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3

Quantifying Cadmium in Tissue Samples

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Cadmium content in tissues was analyzed by graphite furnace atomic absorption spectrophotometry (GFAAS) (PerkinElmer AAnalyst 600), according to the technique described by Christian, 1969 [33 (link)] and using the conditions described by Eller and Haartz (1977) [34 (link)]. The brain regions were dissected out in parietal cortex (Cx), striatum (St), hippocampus (Hp), and cerebellum (Ce) [35 (link)]. Tissue samples were digested in 1 mL of concentrated HNO3. Calibration curves were constructed using an aqueous Cd reference standard (GFAA mixed standard, PerkinElmer). As biological-matrix external standard, we used nitric acid-digested bovine liver (NIST 1577b) standard reference material, and this certified standard was analyzed in every analytical session; values obtained from that analysis were 95–105% from those reported by manufacturer. Cd content was expressed as μg of Cd/g wet tissue. All glassware was cleaned by soaking in 3% nitric acid and rinsing several times in deionized water. The limit of quantification for Cd analysis was 0.01 μg/g wet tissue.
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4

Quantifying Toxic Heavy Metals in Serum

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Pb, Hg, and Cd levels in serum were measured as previously described9 (link). Serum cadmium, lead and mercury concentrations were determined by the NEODIN Medical Institute, certified by the Ministry of Health and Welfare of Korea. These tests meet the requirements of the German External Quality Assessment Scheme, the U.S. CDC, and the Korea Occupational Safety and Health Administration program. cadmium and lead were measured by graphite furnace atomic absorption spectrometry (model AAnalyst 600; Perkin Elmer, Turku, Finland) using Zeeman background correction. Total mercury was measured using a direct mercury analyzer (model DMA-80 Analyzer; Bergamo, Italy). Limits of detection (LODs) for lead, mercury, and cadmium were 0.223 µg/dL, 0.05 µg/L, and 0.087 µg/L, respectively. No sample had a value of below a LOD. For internal quality assurance and control, commercial standards (Lyphochek Whole Blood Metals, Bio-Rad, CA, USA) were used as reference materials.
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5

Quantifying Intracellular Platinum Levels

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At least 2 × 105 cells were plated in a 6-cm dish and allowed to attach overnight. The next day, the cells were treated with 50 µM cisplatin for ∼5 h. The cells were washed ×3 with ice-cold PBS and lysed with 35 µl 0.25% triton/water. After a brief processing of samples, platinum (Pt) (ng/mL) was detected from media as well as lysate on a Perkin–Elmer model AAnalyst 600 atomic absorption spectrophotometer. The lower limit of quantification was set to 50. The Pt value (ng/mL) for each sample was normalized to its corresponding protein concentration followed by a ratio of ([Pt]lysate + [Pt]media). The results were expressed as ng Pt/mg protein as fold change of OSC-TMEM16A from control (OSC19-VC). This analysis provides an estimate of intracellular Pt content.
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6

Enhancing Heavy Metal Tolerance in Artemisia

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To assess the role of anaPCS in conferring heavy metal tolerance, A. annua hairy roots transformed with pBI121-anaPCS, non-transformed hairy roots (empty vector), and normal roots were subjected to arsenic (100 µM) and cadmium stress (50 µM) using sodium arsenate (Na2HAsO4·7H2O) and cadmium chloride (CdCl2), respectively, for 5 days. The treatments were divided in to three sets, set 1 with no treatment (control), set 2 with 100 µM of arsenate (Na2HAsO4·7H2O) and set 3 with CdCl2. Each treatment set contains three groups of samples, untransformed hairy roots, transformed hairy roots and normal roots of the plant.
All the experiments were performed in triplicates. The accumulation of arsenic content in treated/non-treated hairy roots and normal roots was determined by the SEM–EDS method and was estimated by atomic absorption spectrometry (Perkin-Elmer A Analyst 600) as described by Kumari et al (2018 (link)).
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7

Determination of Arsenic in Plant Tissues

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The As content in the plant tissues was estimated following the procedure of Rai et al. (2011 (link)). The root and shoot tissue samples were first dried, followed by grinding it into fine powder. Thereafter, the samples were digested in HNO3 and H2O2 (3:1) until the solution turned transparent. The digested root and shoot samples were then used for the estimation of the leaf As content. The As content was estimated using an atomic absorption spectrometer (graphite furnace-fitted) (Perkin Elmer; A Analyst 600).
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8

Cadmium Levels, Diabetes, and Hypertension

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In the KNHANES for these years, subjects were selected randomly for measurement of serum Cd level by gender and age. Serum Cd level were measured by atomic absorption spectrophotometry using a PerkinElmer AAnalyst 600 (PerkinElmer, Turku, Finland). Diabetes Mellitus (DM) was defined as a fasting blood glucose level ≥126 mg/dL, or when this disease had been diagnosed by a physician and the subject had been prescribed a hypoglycemic agent. Hypertension (HT) was defined as having a systolic blood pressure >140 mm Hg or a diastolic blood pressure > 90 mm Hg, or when the subject was taking an antihypertensive drug. Smoking status was categorized by self-reporting as never, ex-, or current smoker. The significant alcohol consumption was defined as >210 in g ethanol/wk for men and >140 in g ethanol/wk for women.[17 (link)]
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9

Measurement of Blood Cadmium Levels

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The heavy metals including blood cadmium were collected into standard evacuated tubes containing sodium heparin. The determination of blood cadmium was measured by graphite furnace atomic absorption spectrometry (AAnalyst 600, PerkinElmer, Turku, Finland) with Zeeman-effect background correction [39 (link),40 (link)]. The cadmium concentration was measured by the Neodin Medical Institute, a laboratory certified by the Korean Ministry of Health and Welfare. The coefficients of variation of the blood cadmium measurement were within 0.95~4.82%. The limit of detection (LOD) for blood cadmium level was 0.056 μg/L in the present study [41 (link),42 (link)]. There were no samples below the LOD level. High BCd level was defined as a BCd concentration >1.874 μg/L, which corresponded to the 90th percentile in the present study.
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10

Trace Element Analysis of Blood

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3 mL samples were placed in BD vacutainer tubes containing EDTA for trace element determination for measuring Pb and Cd (K2 EDTA tube, Vacutainers®; BectonDickinson, Franklin Lakes, NJ, USA). Graphite furnace atomic absorption spectrometry using Zeeman background correction was used for measuring Pb and Cd (Perkin Elmer AAnalyst 600; Perkin Elmer, Turku, Finland). The Neodin Medical Institute, a laboratory certified by the Korea Ministry of Health and Welfare conducted all blood metals analysis. Commercial references were used for internal quality assurance and control (Lyphochek® Whole Blood Metals Control; Bio-Rad, Hercules, CA, USA); the coefficients of variation of lead was 2.65–6.50% and cadmium was 0.95–4.82%. This institute passed the German External Quality Assessment Scheme (operated by Friedrich-Alexander University) and the Quality Assurance Program (operated by the Korea Occupational Safety and Health Agency) for external quality assurance and control. The Ministry of Labor which is one of the designated laboratories for analysis of specific chemicals such as heavy metals and certain organic chemicals certified the institute. The method detection limits of lead was 0.207 µg/dL and cadmium was 0.081 µg/L. All samples exceeded these detection limits.
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