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Polarographic Interaction of Nickel (II) with Ammonium Piperidine-1-Carbodithioate: Application to Environmental Samples | OMICS International
ISSN: 2380-2391
Journal of Environmental Analytical Chemistry
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Polarographic Interaction of Nickel (II) with Ammonium Piperidine-1-Carbodithioate: Application to Environmental Samples

Suvardhan Kanchi1*, Bathinapatla Ayyappa1, Myalowenkosi I Sabela1, Krishna Bisetty1* and Nuthalapati Venkatasubba Naidu2

1Department of Chemistry, Durban University of Technology, Durban, South Africa

2Department of Chemistry, Sri Venkateswara University, Tirupati, A.P, India

*Corresponding Author:
Suvardhan Kanchi
Department of Chemistry
Durban University of Technology
P.O. Box 1334, Durban 4000, South Africa
Tel: +91-9440722881, +27-373-3004/2311
E-mail: [email protected]
Krishna Bisetty
Department of Chemistry
Durban University of Technology
P.O. Box 1334, Durban 4000, South Africa

Received date: January 21, 2012; Accepted date: March 10, 2014; Published date: March 12, 2014

Citation: Kanchi S, Ayyappa B, Sabela MI, Bisetty K, Naidu NVS (2014) Polarographic Interaction of Nickel (II) with Ammonium Piperidine-1-Carbodithioate: Application to Environmental Samples . J Environ Anal Chem 1:107. doi: 10.4172/2380-2391.1000107

Copyright: © 2014 Kanchi S, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.

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Abstract

This paper describes the interaction of nickel (II) with ammonium piperidine-1-carbodithioate (APC) using Direct Current (DC) polarography (DCP) & differential pulse polarography (DPP) at the Dropping Mercury Electrode (DME) in NH4Cl-NH4OH buffer medium at pH 6.0. The polarograms shows a predominant peak for nickel (II)-APC at -1.30 V vs SCE, indicating the production of catalytic hydrogen wave (CHW) due to electrostatic interactions between APC and nickel (II). The interactions were characterized with UV-visible spectrophotometer, FT-IR and cyclic voltammetric techniques. The developed method was applied successfully to determine the nickel (II) levels in leafy vegetables and biological samples with acceptable recoveries.

Keywords

Direct Current Polarography (DCP); Differential Pulse Polarography (DPP); Nickel (II); Ammonium Piperidine-1-Carbodithiate (APC); Interaction; Environmental samples

Introduction

Carbodithioates, a group of small organic molecules with a strong chelating ability towards inorganic species that have been extensively been used in the agricultural industry for more than eighty decades. In recent years their applications have not only become apparent as pesticides and fungicides, but also widely used as vulcanization accelerators in the rubber industry [1]. Moreover, carbodithioates are of biological importance due to their antibacterial, antituberclosis and antifungal properties. The insolubility of metal salts (with the exception of sodium and other alkali and alkaline earth metals) and the capacity of the carbodithioates to form stable metal-complexes are mainly responsible for the extensive use of this class of compounds as superior ligands. Furthermore, carbodithioates exhibit strong binding properties with a number of transition metal ions resulting in stable colored complexes [2]. Nickel is ubiquitous in the environment and an essential metal for animal nutrition, and consequently it is probably essential to humans. Nickel is a relatively non-toxic element; however, certain nickel compounds have been proven to be carcinogenic. The main sources of nickel in aquatic systems include dissolution of rocks and soils, biological cycles, atmospheric fallout, and most importantly industrial processes and water disposal [3].

Over toxicity of nickel may cause skin disorder known as “Nickel-eczema” [4] and other occupational disease [5] especially to workers who handle nickel on regular basis. This skin disorder has also been reported by Cempel and Nikel [6] to appear in people who have great sensitivity to nickel, mostly women, and can be caused by wearing of jewellery made of nickel alloys [6]. While the medical diagnosis is currently established through nickel determination in blood and urine, other studies [7,8] show that disease incidence increased in patients who consume foods rich in nickel, such as oats, nuts, beans and chocolate. Hence, an appropriate knowledge of the nickel content in foods could be of a great interest for the dietary control of nickel-eczema patients. Several analytical techniques such as FAAS [9-13], GFAAS [14-16], ETAAS [17], AFS [18], UV-vis spectrophotometry [19-24] and ICP-OES [25,26] have been proposed for the analysis of nickel (II), but most of these require expensive equipments and time consuming sample preparation procedures. However, the electrochemical analysis of trace amounts of nickel (II) require relatively inexpensive equipment but presents certain difficulties due to their irreversible reduction behavior [27,28] of nickel. Therefore it is needless to say, it has successfully been accomplished using a variety of electro-analytical techniques such as stripping & voltammetric analysis [29-34] including polarography [35].

In this paper, electrochemical and spectrophotometry data are reported on the interaction between nickel(II) and APC, obtained by applying cyclic voltammetry (CV), differential pulse polarography (DPP), FT-IR and UV-visible spectrophotometry. After interaction, the electrochemical behaviour of the complex is studied at DME in presence of NH4Cl-NH4OH medium at pH 6.0 with the view of attaining catalytic hydrogen wave which ensures the credibility of the method for the determination of nickel (II) in selected leafy vegetables and biological samples.

Experimental

Chemicals

All the experiments were performed at 25°C using freshly prepared solutions. Double distilled mercury and double distilled water were used throughout the experiment. The dissolved oxygen in the solutions was removed by passing a 99.99% pure nitrogen gas through the measuring solution in an electrochemical cell for 10-15 minutes. Standard metal ion solution was prepared taking 0.004050 g L-1 of NiCl2.6H2O to get 1 μg mL-1 and adding few milliliters of acid corresponding to the anions of the salts to suppress the hydrolysis. Ammonium Chloride (1 M) (S.D Fine Chemicals, India) was prepared by dissolving 53.49 g of ammonium chloride (Analytical grade) in 1 L with double distilled water. Carbon disulphide and piperidine were also purchased from Merck Chemicals, India.

Reagents

A 5% ammonium hydroxide and 1 % HCl (S.D Fine Chemicals, India) used for pH adjustments were prepared from AnalaR chemicals. Potassium iodate (S.D Fine Chemicals, India) and sodium sulphite (S.D Fine Chemicals, India) were also prepared in double distilled deionised water using Analytical grade samples. Triton X-100 is prepared in w/v basis by weighing 0.2 g and dissolving it to 100 mL with double distilled water Gelatin (Difco laboratories, USA) was prepared by weighing accurately 0.1250 g and dissolving to 25 mL with doubly distilled water. APC was synthesized according to procedure reported in literature [1,36-43].

Instrumentation

The current-voltage curves were recorded using a DC Polarographic analyzer, model CL-357 coupled with model LR-101 strip chart recorder manufactured by Elico Private Ltd (Hyderabad, India). Effects of mercury height on polarographic currents were studied using DC recording polarograph model CL-25 of Elico Pvt Ltd, Hyderabad. DPP & Cyclic voltammetric studies were performed with a 797 VA Computrace (Metrohm, Herisau, Switzerland). All pH measurements ranging from 2 to 10 were done using pH meter, model LI-120 (Elico Pvt. Limited, India). An IR spectrum was obtained using a Varian 800 FT-IR Scimitar Series supplied by SMM Instruments [Durban, South Africa (SA)].

Electrochemical measurements

A measured volume of the NH4Cl-NH4OH buffer and APC solution at optimum pH were made in a 100 mL in beaker with distilled water and then adequate amount was transferred into the electrochemical cell followed by addition of the required sample or standard nickel (II) solution. The dissolved oxygen was expelled by bubbling pure nitrogen through the analyte solution for 15 min. Polarograms of the solution were recorded using DC/DP polarography at -1.30 V vs SCE in ammonium chloride-ammonium hydroxide medium. APC or simple metal ions [nickel (II)] in the medium do not give any current signal at the potential mentioned.

Real sample preparation

To test the validity of the proposed method, different samples of environmental importance were collected and processed for the analysis of nickel (II) after interaction with APC in the presence of NH4Cl-NH4OH medium. The evolved catalytic hydrogen currents were determined using DC/DPP.

Vegetable samples

5.0 g of Hibiscus cannabinus (Gongura), Celosia argentea (gurugaku), Spinacia oleracea(palaku), Amaranthus graecizans (Sirraku) and Alternanthera sessilis (ponagantaku) samples were collected from the local market. The collected samples were digested by dry ashing method followed by dissolution to 25 mL with double distilled water. The metal ions that are commonly associated with nickel (II) are included in the preparation of the standards. Aliquots of the above sample solution were taken into a beaker and the quantitative experimental conditions were maintained as already described. The polarograms were recorded after filtering the precipitates of interfering ions and after spiking the solution with a known amount of nickel (II).

Milk samples

A 100 mL sample of milk was added drop wise into a crucible and heated to 450 -500°C for 1 hr to remove moisture and evaporate it without frothing. The obtained dark ash was dissolved in 3 mL of concentrated HNO3 and evaporated, and again dissolved in the 3 mL of dilute HNO3. The sample was filtered and the filtrate was made up to the mark in a 25 mL volumetric flask with deionized water. Required volume of the sample was used for the analysis of nickel (II) using aforesaid procedure.

Blood samples

Blood samples obtained from local sources were digested by mixing 30 mL of sample, 10 mL of deionised water, 18 mL concentrated HNO3 and 5 mL of 30% H2O2 in a 100 mL beaker. The mixture was heated while stirring until the volume decreased to half than filtered. The filtrate was made up to a 250 mL volumetric flask with deionized water for the analysis of nickel (II) using the aforesaid procedure.

Results and Discussion

Electrochemical behavior of nickel (II)-APC complex

Cyclic voltammetric studies: Cyclic voltammetric studies have been performed to illustrate and validate the promising mechanism between nickel (II) and APC in aqueous solution using hanging mercury dropping electrode (HMDE) with a scan rate of 0.09 mV/sec. Figure 1A shows cyclic voltammogram of APC in a 0.4 M NH4Cl-NH4OH electrolyte solution of pH 6.0. On the other hand Figure 1B shows cyclic voltammogram of nickel (II)-APC complex. In the case of APC, two predominant reversible peaks at E1/2 of - 0.48 V and - 0.68 V, while Figure 1B shows only one reversible peak at E1/2 = -0.5. The shift in potential and disappearing of the first peak confirms that there are interactions between nickel (II) and APC. Based on this investigation, praise worthy mechanism is proposed as follows: The sulphur atoms of APC involves in the co-ordination of nickel (II).

environmental-analytical-chemistry-Cyclic-voltammograms-nickel

Figure 1: Cyclic voltammograms for (A) 2.0 mM APC (B) 2.0 mM APC + 2.0 μg mL-1 nickel (II) in 0.3 M NH4OH-NH4OH at pH 6.0.

DC/DPP studies: In this methodology, nickel (II) forms a complex with APC, which subsequently absorb onto the DME/HMDE working electrodes during the deposition step. During the polarographic scan, nickel(II)-APC [Ni+2-APC]ads complex is reduced to [Ni0-APC]ads which undergoes protonation by accepting proton from the solution [Ni0–APCH+]ads in the adsorbed state, followed by the reduction to liberate hydrogen in presence of mercury electrode, as shown in equations 1-3 below [1,36]:

M2+RS + 2e- + H+ → M0RSH+ (1)

M0RSH+ + H2O → H+ + M0RS (2)

H+ + e-→ 1/2 H+(3)

M = Nickel (II), RS = Carbodithioates

Therefore, oxidation of APC at the HMDE is represented as which was in agreement with the earlier reports in the literature [1,36,44].

RSH + Hg → RSH + e- + H+

RS = Carbodithioates

The typical DC/DPP polarograms recorded at E1/2 = -1.30 V for nickel (II)-APC complex system are shown in Figure 2A and 2B.

environmental-analytical-chemistry-Polarographic-curve-Nickel

Figure 2A: Polarographic curve of nickel (II) in NH4Cl-NH4OH medium in the presence of APC (a) 0.4 M NH4Cl, pH ~6.0 (b) a + 2.0 mM APC (c) a + 2.0 μg mL-1 Nickel (II) d) b + 2.0 μg mL-1 nickel (II).

environmental-analytical-chemistry-nickel-medium-Current

Figure 2B: Obtained DPP curves of nickel (II) in NH4Cl-NH4OH medium in the presence of APC using standard addition method [Conditions:-Current range: 100 μA, Scan rate: 6 mV/S, Pulse amplitude: 50 mV, Drop time: 1 Sec, Nickel (II): 2.0 μg mL-1].

Spectrophotometric studies on nickel (II)-APC complex

UV-Visible studies: UV–visible spectrophotometric techniques have often been used to study the interaction mechanism between metal and ligand [1,35-43]. Figure 3 shows the UV spectra of nickel (II) and APC before and after their interaction. The spectrums of this figure depict that before the interaction of nickel (II) with APC, there is less or no absorption while after the interactions, a sharp absorption peak is observed at about 230 nm confirming the interaction. Therefore, it could be concluded that nickel (II) interacts with APC and both the results of electrochemical studies and UV-Vis spectrophotometry are in agreement in this regard.

environmental-analytical-chemistry-Absorption-spectra-interaction

Figure 3: Absorption spectra of before and after interaction of nickel (II) with APC [Conditions: APC= 2.0 mM, Nickel (II) = 2.0 μg mL-1].

FT-IR studies

In Figure 4, the IR spectras of the pure APC and nickel (II)-APC complex system are shown. Here, a single band of strong intensity was observed in the range 1022-1001 cm-1 which may be attributed to υ(C-S) vibration. A negative shift of 83-28 cm-1 in comparison to the corresponding band in the free ligand indicates that the APC coordinates with the nickel (II) through sulphur atoms. The presence of an only C-S band can be due to the greatest contribution of the resonance form (RN+CS2-) in the adducts and the complex, thus suggesting symmetrical bidentate binding of the carbodithioates moiety.

environmental-analytical-chemistry-FT-IR-spectra-nickel

Figure 4: FT-IR spectra of before and after interaction of nickel (II) with APC.

Optimization of analytical parameters

Effect of pH: pH plays vital role in the interaction of nickel (II) with APC and their catalytic hydrogen waves production from the complex. The effect of pH ranging from 5.0 to 10.0 on solutions containing 2.0 μg mL-1 of nickel (II) in 0.4 M buffer solution was tested. With increasing pH, the height of the CHW increased, after attaining a maximum peak current at pH 6.0, the wave height decreased with further increase in pH. The maximum wave heights of the polarograms are selected as optimum pH for further studies as shown in Figure 5.

environmental-analytical-chemistry-Effect-interaction-buffer

Figure 5: Effect of pH on interaction of nickel (II) with APC [conditions: supporting buffer = 0.4 M, APC= 2.0 mM, Nickel (II) = 2.0 μg mL-1].

Effect of buffer concentration

The effect of NH4Cl-NH4OH (buffer) was studied in the range of 0.1 to 0.8 M on the nature of current-voltage curves at DME/HMDE obtained after interaction of nickel (II) with APC, keeping the nickel (II) ion concentration at 2.0 μg mL-1 and APC at 2.0 mM. The polarograms were well defined in NH4Cl-NH4OH of 0.4 M and the peak height is decreased beyond this concentration as shown in Figure 6.

environmental-analytical-chemistry-supporting-buffer-nickel

Figure 6: Effect of supporting buffer concentration on interaction of nickel (II) with APC [conditions: pH=6.0, APC= 2.0 mM, Nickel (II) = 2.0 μg mL-1].

Effect of APC concentration

The solution of nickel (II) and ammonium chloride containing fixed quantities of 2.0 μg mL-1 and 0.4 M respectively and an APC concentration varied from 0.5 to 6.0 mM, while the pH of the solution was maintained at 6.0. The peak current does not vary linearly with concentration of APC which was a typical characteristic nature of catalytic hydrogen wave (Figure 7). From the results it is observed that the wave height increased linearly with increase in APC concentration up to 2.0 mM. With further increase in APC concentration, the independence of the wave height from the concentration is unveiled as, it become relatively stable after 2.0 mM. The concentration of the APC was fixed at maximum wave height for quantitative studies. The peak potential of the catalytic wave shifted more towards a negative potential upon increasing the APC concentration, until maximum current response was observed and remained constant beyond the respective concentrations. Plot of [APC]/ip Vs [APC] was a straight line (Figure 8) and confirms that adsorption phenomenon was involved in the electrode reaction process.

environmental-analytical-chemistry-concentration-interaction-nickel

Figure 7: Effect of APC concentration on interaction of nickel (II) with APC [conditions: pH=6.0, Supporting buffer=0.4 M, Nickel (II) = 2.0 μg mL-1].

environmental-analytical-chemistry-Langmuir-adsoption-isotherm

Figure 8: Langmuir adsoption isotherm plot after interaction of nickel (II) with APC [conditions:- pH=6.0, Supporting buffer=0.4 M, APC=2.0 mM, Nickel=2.0 μg mL-1].

Effect of nickel (II) concentration

At fixed concentrations of APC at 2.0 mM,, buffer at 0.4 M and pH at 6, the metal ion concentration was varied between 0.5 to 6.0 μg mL-1 and it proportionality to the peak current was studied. The results obtained are shown in Figure 9. The peak current increased linearly with nickel (II) concentration in the range 0.5 to 6.0 μg mL-1. The method suggests that the quantification of trace and ultra-trace levels of nickel (II) was possible in unknown samples. No changes were observed in the shape of the wave throughout the selected range of nickel (II) concentration.

environmental-analytical-chemistry-nickel-concentration-buffer

Figure 9: Effect of nickel (II) concentration on interaction of nickel (II) with APC [conditions: pH=6.0, Supporting buffer=0.4 M, APC=2.0 mM].

Foreign ion effect

Different metal ions and salts were added individually to a 20 mg of nickel (II) solution and analysis was carried out as per to the aforesaid electrochemical measurements procedure. The tolerance limit was set as ± 2% error in the peak current for the determination of nickel (II). Among all the metal ions examined, most could be tolerated up to 1 mg, except for 35 mg of copper (II), 40 mg of aluminum (III) and 20 mg of iron (III) ions. However, these could easily be masked by addition of 0.5 g sodium fluoride, 7 mg of trisodium citrate for aluminum (III) & iron (III), 0.1 g of thiourea and 0.1 g of Na2S2O3 for copper (II). Among the salts (anions) examined, most could be well tolerated to above mg levels, except for 15 mg of EDTA. The results obtained are depicted in Table 1. Accordingly the developed method is highly selective and may be successfully applied for the determination of nickel (II) in leafy vegetables and biological samples.

Ions Tolerance limits(mg)
Pb+2 15
Co+2 0.5
Os+8 0.7
Cu+2 15, 0.40
Ag+1 10
Mo+6 5.0
Cr+6 7.0
Hg+2 0.5
V+5 2.0
Fe+3 0.00030, 0.30**
Ru+3 1.5
Zn+2 5.0
Sb+3 7.0
Cu+2 0.00025, 0.20*
Al+3 0.00030, 5.0**
Bi+3, Rh+3 0.5
Cd+2 9
U+6, Cr+3 3.0
Ga+3,Se+6 2.0
KI, NaF 500
Na2EDTA 0.0002
KSCN 20
CaCl2, Na2S2O3 150
K2SO4 250
CH3COONa.3H2O 750
KNO3, NH4Cl 1000
KNaC4H4O6.4H2O 45
Na3C6H5O7 Na2C2O4 15
*Masked with 0.5 g NaF and 10 mg trisodium citrate **Masked with 0.3 g thiourea and 0.1 g Na2S2O3

Table 1: Effect of foreign ions on the determination of nickel (II) in various water samples

Method validation

The analytical method was validated considering different validation parameters including selectivity, linearity, limit of detection (LOD), limit of quantification (LOQ), accuracy, precision (inter-day precision & intra-day precision) and stability for the analysis of nickel (II).

A linear trend between the peak current and nickel (II) concentration is observed in the range of 0.1-7.0 mg L-1 with the regression co-efficient of 0.998. The coefficient of determination (r2) obtained from the regression line was 0.999. The electrochemical methodology described in this paper was based on a calibration curve for quantitative analysis, and the corresponding limit of detection (LOD) and limit of quantification (LOQ) are determined and found to be 0.25 and 1.59 mg L-1 respectively.

The accuracy of the developed method was performed using synthetic samples as shown in Tables 2,3. Synthetic samples were prepared with known amounts of standard solutions (0.2, 0.4, 0.6, 0.8, 1.0 and 1.2 μg mL-1). It is evident in tables 2 and 3 that the method had good accuracy, which was in the range of 92.10-99.57 % within the concentration range investigated for the determination of nickel (II) in various water systems. The precision of the method was also validated based on the relative standard deviation (RSD) measuring repeatability (n=5) at different concentrations. The % RSD values were less than 2% and illustrated a good precision of the analytical method (Tables 2 and 3). In addition to the accuracy results which confirmed the selectivity of the method, %RSD values were lower than 1.89%, confirming a good precision of this method for the analysis of nickel (II). The stability of pure APC and nickel (II)-APC complex were determined by storing the samples at room temperature and in refrigerator for one to seven days. The results of stored sample solutions are analyzed and compared with those of a freshly prepared standard at each time interval. No degradation in the APC and nickel (II)-APC was observed during from day one to day five. After day five, ± 0.5/0.7 % decrement in the absorbance and peak current were observed, which indicated the stability of the complex and samples can be stored for at least one week prior to analysis.

Samplea Scientific/Local name DCP method DPP method t-test* f-test**
Ni(II), μg mL-1 Recovery(%)± RSDb Ni(II), μg mL-1 Recovery(%)±RSDb
Hibiscus cannabinus/ gongura 1.048 96.40±1.62 1.052 96.80±1.70 1.62 0.25
Celosia argentea/ gurugaku 1.102 97.55±1.39 1.100 97.40±1.54 1.19 0.12
Spinacia oleracea/ palaku 1.258 98.00±1.55 1.250 97.98±1.62 1.26 0.79
Amaranthus graecizans/ Sirraku 0.951 99.10±1.20 1.027 99.25±1.40 1.82 0.20
Alternanthera sessilis/ ponagantaku 1.209 98.80±1.86 1.210 99.10±1.15 1.40 0.46
Conditions: pH=6.0, Supporting buffer=0.4 M, APC=2.0 mM a5 mL of the concentrated sample is used, bRelative Standard Deviation (n=6),*1% level of significance, **5% level of significance. All samples were spiked with 0.5μg mL-1 nickel (II) standard

Table 2: Analysis of nickel (II) after interaction with APC in leafy vegetable samples

Samples DCP method DPP method t-test* f-test**
Ni(II) Added, μg mL-1 Ni(II), Found μg mL-1 Recovery(%)±RSDb Ni(II), Found μg mL-1 Recovery(%)±RSDb
Milk samples
1 0.2 0.250 92.55±1.50 0.263 95.75±1.45 1.48 0.23
2 0.4 0.437 93.40±1.62 0.440 93.20±1.20 1.26 0.10
3 0.6 0.690 99.50±1.33 0.690 99.50±1.30 1.19 0.37
4 0.8 0.866 98.15±1.05 0.872 98.55±1.73 1.56 0.55
5 1.0 1.055 98.82±1.20 1.100 99.00±1.55 1.37 0.62
6 1.2 1.284 99.57±1.73 1.290 99.70±1.10 1.94 0.40
Blood samples
1 0.2 0.246 94.66±1.27 0.248 94.80±1.48 1.29 0.24
2 0.4 0.444 92.10±1.49 0.438 94.75±1.35 1.53 0.18
3 0.6 0.682 98.50±1.66 0.690 99.00±1.26 1.48 0.36
4 0.8 0.873 98.75±1.50 0.875 98.80±1.57 1.24 0.12
5 1.0 1.140 94.00±1.35 1.155 95.55±1.62 1.67 0.47
6 1.2 1.238 97.15±1.73 1.243 98.60±1.70 1.70 0.50
Conditions:- pH=6.0, Supporting buffer=0.4 M, APC=2.0 m a5 mL of the concentrated sample is used, bRelative Standard Deviation(n=6), *1% level of significance, **5% level of significance

Table 3: Analysis of nickel (II) after interaction with APC in biological samples

Analytical applications

To test the validity of the proposed method, various leafy vegetables and biological samples were collected for the determination of nickel (II) after complexation with APC in the presence of NH4Cl-NH4OH medium by evolution of peak current in DC/DPP analysis.

The results obtained by this method are further supported by DPP method. The developed method is compared with the DPP method in terms of Student’s‘t’-test and Variance ratio ‘f’-test as shown in Table 2. The analytical data summarized in Tables 2 and 3 suggest that the percentage of nickel (II) recovery ranges from 92.10 to 99.57% with R.S.D (%) = 1.05. The optimization of various parameters for the interaction nickel (II) with APC in the presence of NH4Cl-NH4OH medium is found to be sensitive, selective, specific, reliable and rapid, hence may be successfully applied for the analysis of nickel (II) in leafy vegetables and biological samples.

Conclusions

This paper described the interaction of nickel (II) with APC by electrochemical, UV-visible spectroscopic and FT-IR techniques. From the electrochemical studies by supported with UV–vis and FI-IR studies, it was concluded that there is one electron reaction between nickel (II) and APC with a highly stable complex. The optimized parameters lead to the development of analytical techniques for the determination of nickel (II) in trace and ultrace levels in various water systems. The present method is highly sensitive, selectivity, accurate and precise for the analysis of nickel (II). The limit of detection of the developed method is superior when compared with already reported methods. The CHW method developed is free from interferences of many commonly associated metal ions with nickel (II) which usually requires separation techniques and therefore reported here can be placed among the most sensitive and rapid methods of analysis of environmental samples.

Acknowledgement

S Kanchi is highly grateful to the Durban University of Technology for the financial support to carry out this work.

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