An Alternative Method for the Preparation of Bis(Dimethylglyoximato)Nickel(II) Synthesis and Reactivity in Inorganic and Metal-Organic Chemistry: Vol. Reported that normal human plasma contains 0.012-0.085 µg mL-1 of nickel (II). Nickel is one of the important alloying element for steel and cast iron. A nickel metallo enzyme is an essential micronutrient 4-6 for plants arose from ureases. Literature survey indicated that several spectrophotometric methods 7-17 were reported for the. Note: The precipitate is Nickel Dimethylglyoxime (NiDMG) Mass of Precipitate in Sample = Crucible + Precipitate Mass Dry - Crucible Mass = 31.1754 - 30.9409 = 0.2345g Figure 1. Molecular Structure of Nickel Dimethylglyoxime (Source: OUP, 2004).
The Gravimetric Determination of Nickel INTRODUCTION Nickel(II) forms a precipitate with the organic compound dimethylglyoxime, C4H6(NOH)2. The formation of the red chelate occurs quantitatively in a solution in which the pH is buffered in the range of 5 to 9. The chelation reaction that occurs is. To obtain a gravimetric determination of nickel using dimethylglyoxime: Weigh and measure a sample so that not over 100 mg. Of nickel present. Add 10 cc’s of nitric acid.5 to.1 grams of potassium chlorate and digest on the steam plate adding more potassium chlorate if necessary to effect solution. Evaporate to dryness. Cool slightly and add 5 cc’s of HCl. And again evaporate to dryness.
ARTICLE
A selective flotation-spectrophotometric method for the determination of nickel using dimethylglyoxime
Hamid Hashemi-Moghaddam*
Department of Chemistry, Islamic Azad University Damghan Branch, PO Box 36716-39998, Damghan, Iran
ABSTRACT
A simple and selective method for separation and preconcentration of nickel has been developed. The method is based on the flotation of a complex of Ni and dimethylglyoxime (DMG) at the aqueous solution-n-hexane interface. The complex was separated and Ni determined spectrophotometrically by DMG after addition of oxidizing agent. The quantitative flotation of the complex was possible in the pH range of 9-12. The method is simple and free from the interference of all cations and anions and has a wide linear range. The procedure was successfully applied to the determination of trace amounts of nickel in well water and waste water in coating plant. The method's accuracy was investigated by using standard reference materials alloys (NIST 864) and by spiking the samples with different amounts of Ni2+.
Keywords: flotation, spectrophotometry, dimethylglyoxime, nickel
RESUMO
Um método simples e seletivo para a separação e pré-concentração de níquel foi desenvolvido. O método é baseado na flotação de um complexo de Ni e dimetilglioxima (DMG) na interface de uma solução aquosa com n-hexano. O complexo Ni-DMG foi separado e determinado por espectrofotometria. A flotação quantitativa do complexo foi possível no intervalo de pH de 9-12. O método é simples e livre da interferência de todos os cátions e ânions e apresenta um grande intervalo linear. O procedimento foi aplicado com sucesso na determinação de traços de níquel em águas de poços e águas residuais de um processo de eletrodeposição. A exatidão do método foi avaliada usando material de referência certificado (NIST 864) e enriquecendo as amostras com diferentes quantidades de Ni2+.
Introduction
Nickel is an important constituent of several steel alloys. Its determination is required to control both raw material and industrial products.1 In addition it is readily encountered in the environment, which enters from land-based resources, such as oxidic and sulfide ores or industrial sources, such as spent catalysts, alloy scrap, sludge, dust, and wastewater.2
Dimethylglyoxime (DMG) is widely used and for the spectrophotometric determination of nickel3,4 it has also been used for separation and preconcentration of Ni by liquid-liquid extraction5 or solid phase extraction6-8 but all of these separation methods suffer from lack of selectivity. For example, metal ions such as Ni(II), Pb(II), Mn(II), Bi(III), Co(II), Cd(II), Zn(II), and Fe(II) could interfere at concentrations higher than 5 mg L-1 in solid phase extraction of Ni2+ using DMG as a complexing agent.8
This paper deals with a selective and simple method for separation and preconcentration of Ni with DMG.
Flotation spectrophotometry allows one to preconcentrate the trace elements in various materials.9–24 Primary investigations showed that the none of two usual complexes of Ni and DMG could not float completely in interface of liquid and organic phase due to solubility in water and organic phase of Ni(Dm)32- and Ni(HDm)2, respectively. Thus a different complex of Ni and DMG was studied. As it observed, in more basic pHs, a different complex could be formed that is floated in interfaces of two phases. This complex is formed very fast and metal ions (e.g., Fe2+, Co2+ and Cu2+) which form colored, water-soluble complexes with dimethylglyoxime do not interfere in this condition. Simple spectrophotometric determination of trace amounts of Ni in complex environmental samples by DMG could be possible after preconcentration and separation of Ni(II) with this method.
Experimental
Materials
The solutions were prepared with freshly deionized water and chemicals of analytical reagent grade. The 1.000 g L-1 Ni standard stock solution was prepared by dissolving 6.7300 g (NH4)2Ni(SO4)2•6H2O (Merck, Germany) in water containing 2 mL of concentrated H2SO4 and completing the volume to one liter with water. The 2% (m/v) dimethylglyoxime solution was prepared by dissolution of an appropriate amount of reagent in 250 mL of a 2.0 mol L-1 NaOH solution. Potassium persulfate, 4% (m/v) solution, freshly was prepared. Sodium borate- boric acid buffer (pH 10.0). This solution was prepared by dissolving 12.78 g of sodium borate (Merck) in 100 mL of water, followed by the addition and dissolution of 6.18 g of boric acid (Merck) and was diluted to 1000 mL.
The standard reference material with certified values was the NIST 864 (New York, USA) Inconel 600. The materials were dissolved in concentrated HCl and HNO3 acids. 25
Sample collection
Wastewater samples were collected from a nickel-chrome electroplating plant in Damghan, Iran. The samples were put in plastic containers initially rinsed three times with the wastewater.
Sample preparation
The waste water and well water samples were filtered through a 0.45 μm membrane filter paper. An aliquot of the filtered sample (10 mL) was put into a 250 mL conical flask and digested with 5 mL mixture of concentrated nitric acid (65%, v/v) and perchloric acid (70%, v/v). When digestion was complete, 10 mL of 0.5 mol L-1 HCl was added to redissolve the residue and the resultant solution filtered into a 50 mL volumetric flask.
Apparatus
Cary 100 (Varian, Australia) spectrophotometer with a quartz cell (10.0 mm optical path) was employed for nickel determinations. A pH meter, Metrohm744A, was used for pH measurements.
Procedure
To the solution containing not more than 50 mg of Ni, 5 mL of 0.02 mol L-1 EDTA solution and 10 mL of boric acid/sodium borate buffer was added. The solution was transferred to a 250 mL separating funnel; then 2 mL dimethylglyoxime (2%, m/v) and 10 mL n-hexane were added sequentially. The funnel was stoppered, vigorously shaken for 2 min, then left to rest for a few minutes. As soon as the floating layer had settled at the organic interface, both the upper organic and lower aqueous layers were discarded by slowly opening the cock of the funnel. Then, for dissolving the floated complex, which was completely adhering to the inner walls of the funnel, 4 mL 2 % (m/v) of DMG, 1 mL of 4% (m/v) persulfate solution and 2.5 mL of concentrated NH3 solution were added successively. The obtained solution was quantitatively transferred into a 25 mL flask and diluted to the mark with water. Finally, the absorbance at 445 nm against water was measured.
Results and Discussion
The reaction between Ni and dimethylglyoxime is a well established process. DMG reacts with Ni ions in a neutral or ammoniacal medium to form a pink, flocculent precipitate which has been the basis of the well known gravimetric method for determining nickel. The nickel dimethylglyoximate chelate is soluble in CHCI3 and other non polar organic solvents. The extraction of Ni(HDm)2 is primarily important in the separation of nickel, but relatively large quantities of nickel have been determined by means of the pale yellow chloroform solution of Ni(HDm)2. Also in an alkaline medium and in the presence of oxidants, nickel forms a brown-red, water soluble DMG-complex, which is the basis of the very popular method for determining nickel. In this complex, nickel is in the IV oxidation state, and the anionic complex has the formula Ni(Dm)32-.3 Primary investigation showed that any of each two complexes could not float completely in the interface of liquid and organic phase because of solubility in water and organic phase of Ni(Dm)32- and Ni(HDm)2, respectively. Thus a different complex of Ni and DMG was studied. As it was observed, in more basic pH and with DMG, which dissolved in NaOH solution a different complex could be formed that is floated in interfaces of two phases.
Ni2+ + 2DH2 → Ni(DH)2 + 2H+
Ni(DH)2 + 2OH- → [NiD2]2- + 2H2O ( in alkaline solution)
Ni2+ + 2DH2 + 2OH- → [NiD2]2- + 2H+ + 2H2O
Though the spectroscopic evidence indicated the presence of various nickel-DMG complexes with different ratios of metal to ligand (1:2 and 1:4) in solution, the difficulties still encountered in the identification of a 'metastable' complex are not early understood.26
Routeros 6 iso crack. The various parameters such as pH, shaking times and the concentration of the ligand, which influence the flotation and spectrophotometric determination of nickel, were optimized.
Optimization
The effect of the pH on the flotation of the complex was investigated by varying the pH of Ni(II) solution (1.7 × 10-6 mol L-1) in the range from 4 to 12 before the addition of the organic phase. The results in Figure 1, indicates that the maximum absorbance occurs at pH above 9. The decrease in absorbance at lower pH values was attributed to the protonation of the weakly basic coordination group of ligand and also because in neutral pH Ni(HDm)2 could be formed, which is dissolved somewhat in n-hexane. In the subsequent work, pH 10 was selected.
Fast formation of Ni-DMG complex and no solubility of complex in n-hexane are depending on the kind of DMG solvent. If DMG is dissolved in ethanol, efficiency of flotation would be low but flotation efficiency increase in more basic solvents because of increasing polarity of Ni-DMG complex. The effect of the agitation time on the flotation was studied by varying the shaking time between 10 and 180 s. The result of the investigation indicates that the time of 60 s is sufficient for the quantitative formation and flotation of the complex.
The effect of the DMG concentration on the flotation of the complex was studied over the concentration range of 0.1 × 10-5 to 1 × 10-3 mol L-1. As shown in Figure 2, maximum absorbance occurs to DMG concentrations above 2 × 10-4 mol L-1. Since by increasing the concentration of Ni(II) ions, a greater amount of DMG was required, a solution with 4 × 10-4 mol L-1 DMG was chosen for further investigations.
Flotation of the complex was investigated with several organic solvents. It was found that the absorbance depends on the solvent. For example, at the optimum conditions, the absorbance values for the flotation of 4 × 10-6 mol L-1 Ni(II) with cyclohexane, n-heptane, and n-hexane were 0.438, 0.462 and 0.486, respectively. In addition, quicker separation between the phases was observed using n-hexane. Thus, it was chosen for the further investigations. Furthermore, the complex is dissolved somewhat in solvent such as, toluene, xylene and chloroform.
A possible concern was whether a high enrichment factor could be realized. This was investigated by carrying the flotation processes and varying the volume of the aqueous solution between 20 and 250 mL, while maintaining the amounts of nickel and the organic-phase constant. It was found that the flotation process was quantitative over the range of 20-150 mL of the aqueous phase. A higher volume, however, resulted in a decrease in the efficiency of the flotation process.
Analytical performance
Under the optimum conditions, a linear calibration curve was obtained for Ni(II) over the range from 1 × 10-6 to 2 × 10-5 mol L-1, with the correlation coefficient (r) of 0.9973 (A = 5.42 × 104 [Ni] – 0.0463, where A is the absorbance and [Ni] is the concentration in mol L-1). The apparent molar absorptivity at 445 nm was 5.42 × 104 L mol-1 cm-1 for a 100 mL aliquot of the aqueous phase and a path length of 1 cm. The relative standard deviation (n = 6) at 4 × 10-6 mol L-1 of Ni2+ for a 100 mL sampling volume was 2.7% and the detection optical limit is defined as the sample concentration giving a signal equal to the blank average signal (25 blank) plus three times the standard deviation of the blanks was found to be 1.7 × 10-7 mol L-1.
Interferences
The most significant interferences for the nickel determination with DMG are Cu2+, Co2+ and Fe2+ that produce stable complexes with the organic reagent. But, for example, although the copper complex of dimethylglyoxime is certainly more stable thermodynamically than the nickel complex, the latter is far more insoluble because of the special features of the packing of discrete molecules in the crystal lattice which provides strong axial Ni–Ni bonds through the lattice.26 So, in this flotation method, complexes of Cu2+, Co2+ and Fe2+ with DMG could not be floated in interface of two phases and have not any interference in the determination of Ni2+. In the case of palladium, it produces a yellow precipitate from weak acid solution however it could be floated partially but this yellow complex could not interfere in flotation spectrophotometric determination of Ni by dimethylglyoxime. In addition, usually the concentration of Pd is very low in environmental samples. Formation of insoluble compounds was prevented in the alkaline medium by adding 5 mL of 0.02 mol L-1 EDTA solution.
Application
To validate the methodology, the proposed method was applied to different environmental samples for Ni determination. The wastewater was collected from an electroplating plant. Along with the samples, several known amounts of Ni(II) were spiked to examine the reliability of the method (Table 1).
Furthermore, the accuracy of the method was investigated by analysis of standard reference materials alloys (NIST 864) by flotation spectrophotometry method. The certified Ni was 73.10%, and Ni found was 73.04 ± 0.08%, in good agreement with the certified value at the 95% confidence level.
Conclusion
In a different way, a complex of Ni with dimethylglyoxime was formed in order to separate and preconcentrate Ni ions by flotation spectrophotometric method. High tolerance to interference matrix ions in different samples, selectivity and a low cost are the main benefits of the presented method. Low detection limit and high tolerance to interferences from the matrix allow application of the proposed procedure for Ni determination in a large range of samples. Besides of presenting an analytical method for nickel determination, preparation and separation of new complexes of Ni and DMG is possible with this method.
Though the spectroscopic evidence indicated the presence of various nickel-DMG complexes with different ratios of metal to ligand (1:2 and 1:4) in solution, the difficulties still encountered in the identification of 'metastable' complex are not early understood.27
Acknowledgments
We are grateful to the Pars Material Research and Testing (PMRT) for valuable technical assistance.
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Submitted: August 18, 2010
Published online: February 15, 2011
*e-mail: h.hashemimoghadam@damghaniau.ac.ir
Supplementary Information
Figure S1 - Click to enlarge
Figure S2 - Click to enlarge