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Nickel 2 chloride hexahydrate nicl2 6h2o

Manufactured by Merck Group
Sourced in Canada, United States

Nickel (II) chloride hexahydrate (NiCl2·6H2O) is an inorganic compound that consists of nickel, chlorine, and water molecules. It is a green crystalline solid that is soluble in water. The compound is commonly used in various laboratory applications as a source of nickel ions.

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2 protocols using nickel 2 chloride hexahydrate nicl2 6h2o

1

Comparative Evaluation of Metal Oxide Nanoparticles

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A total of 21 individual uncoated and coated ZnO, CuO, MnO2, NiO, Al2O3, CeO2, TiO2, and Fe2O3 MONPs were investigated in this study. The material purity ranged from 97.8 to 99+%, and the primary particle size ranged from 10 to 60 nm. Table 1 lists the catalog numbers (Cat#), the vendor, and the physicochemical characteristics of MONPs as provided by the manufacturer.
The study also included the uncoated bulk analogs of ZnO, CuO, MnO2, NiO, Al2O3, CeO2, TiO2, and Fe2O3 (Table 2) and the dissolved metal analogs to evaluate the effects of particle size and solubility on the potential genotoxicity. ZnCl2 (Cat#Z0152), CuCl2 dihydrate (CuCl2·2H2O, Cat#C3279), manganese (II) sulfate monohydrate (MnSO4·H2O, Cat#M7899), nickel (II) chloride hexahydrate (NiCl2·6H2O, Cat#N6136), aluminum (III) chloride hexahydrate (AlCl3·6H2O, Cat#A0718) and cerium (III) chloride heptahydrate (CeCl3·7H2O, Cat#228931) were obtained from Sigma–Aldrich (Oakville, ON, Canada). The physicochemical characterization, the results of cell viability and DNA damage assay (as evaluated by comet assay) for ZnO NPs (Cat#US3580), CuO NPs (Cat#544868), TiO2 NIST NPs (referred to as “uncoated TiO2 NPs”), ZnO MPs (Cat#US1003M), CuO MPs (Cat#US1140M), TiO2 MPs (Cat#US1017M), ZnCl2 and CuCl2 were previously reported [34 (link)] and are included in this study for comparison purposes.
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2

Nickel Toxicity Evaluation in Aquatic Life

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Nickel(II) chloride hexahydrate (NiCl 2 6H 2 O) (Sigma-Aldrich, St. Louis, MO, USA) was dissolved in bottled spring water to prepare a stock solution of 1.5 g/L NiCl 2 . The test solutions were prepared directly from this stock solution before use. Larvae and adults were subjected to two periods of treatment, acute (short-time exposure) and subchronic (long-time exposure), and were exposed to four different nominal concentrations of NiCl 2 (0.025, 2.0, 5.0, and 15.0 mg/L in water) or water (control group). The nickel concentrations were chosen based on CONAMA legislation (National Environment Council -regulation No. 357, March 25th, 2005) , which recommends a maximum total nickel concentration of 0.025 mg/L in fresh water bodies and 2.0 mg/L in effluent water (CONAMA, 2005; CONAMA, 2011) . The higher nickel concentrations (5.0 and 15.0 mg/L) were chosen according to Kienle et al. (2008 Kienle et al. ( , 2009)) , who based them on previous studies near industrial sites in unpolluted Canadian lakes and rivers.
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