- Research article
- Open Access
Novel catalytic fluorescence method for speciative determination of chromium in environmental samples
© Adurty and Sabbu; licensee Springer. 2015
- Received: 23 January 2014
- Accepted: 6 January 2015
- Published: 25 February 2015
Thiourea derivatives act as promising chemosensors for sensing transition metal ions. 1-(2-hydroxyphenyl)thiourea (HPTU) is one such chromophore that has potential for metal ion sensing. The current investigation reports the sensing of chromium species using transition metal-oxo-based reaction of 1,2-hydroxyphenylthiourea.
The catalytic effect of chromium (III) and chromium (VI) on the oxidation of HPTU was studied. The reaction was followed spectrofluorimetrically by measuring the fluorescence intensities of the reaction product at λ ex = 416 and λ em = 520 nm, respectively.
Under the optimum analytical conditions, HPTU acts as a chromogenic sensor for the detection of chromium species in nano-gram levels with a determination range of 0.3 to 250 ng/mL.
The methods are fairly sensitive, and the role of activators and sensitizers in enhancing the catalysis was studied. Interference due to various cations and anions in the experiment was investigated. The proposed method was applied to environmental samples for the analysis of chromium content.
- 1-(2-hydroxyphenyl) thiourea
- Speciative determination
- Catalytic fluorescence
The toxicological and biological characteristics of many transition metals like chromium are related to their chemical forms. A great interest in chromium speciation originates from applications of this metal in various industrial activities such as tanning of leather, electroplating, pigment production and wood preservation. Owing to these industrial processes, large amounts of chromium compounds discharge into the environment, which can affect biology and ecology of the environment. Therefore, speciation analysis of chromium is of great importance to assess pollution levels. Chromium mainly exist in two oxidation states, i.e. Cr(III) and Cr(VI). Cr(III) appears to be one of the essential elements for the proper functioning of living organisms, effective in the maintenance of normal glucose, cholesterol and fatty acid metabolism, while water soluble Cr(VI) is toxic to human and living organisms and was found to be carcinogenic. Due to the different toxicities of Cr(III) and Cr(VI), and due to their association in many sample matrices, it is necessary to develop methods where both species can be determined simultaneously (Kotas and Stasicka 2000).
In the past years, various analytical techniques such as atomic absorption spectrometry (AAS) (Karosi et al. 2006; Ren et al. 2007) spectrophotometry (Wu et al. 2007), stripping voltammetry (SV) (Grabarczyk et al. 2006), inductively coupled plasma-mass spectrometry (ICP-MS) (Sun et al. 2006), inductively coupled plasma-optical emission spectrometry (ICPOES) (Schramel et al. 1992), and high performance liquid chromatography (HPLC) (Padarauskas and Naujalis 1998) have been successfully used to determine chromium in various samples. An extensive coverage of the available methods for chromium determination was put forth by Gomez and Callao, including the various types of sample matrices selected for the determination (Gomez and Callao 2006). Reagents such as bis-[2-hydroxy-1-naphthaldehyde] thiourea (Kiran et al. 2008), quercetin (Hosseini and Belador, 2009), chromotropic acid (CA) (Themelis et al. 2006), bis (salicylaldehyde) orthophenylenediamine (BSOPD) (Arancibia et al. 2012 and Soomro et al. 2011), etc. have been used. Methods such as solidified floating organic drop microextraction (SFODME) in combination with graphite furnace atomic absorption spectrometry (GFAAS) (Moghadam et al. 2011), cloud point extraction (CPE) using diethyldithiocarbamate (DDTC) as the chelating agent (Yildiz et al. 2011), solid phase extraction procedure using ICP-MS (Guerrero et al. 2012), fluorescence method using tetraphenylphosphonium bromide (TPP+·Br−) (El-Shahawi et al. 2011), EPA methods 3060A and 3052 (Martone et al. 2013), a disposable dual screen-printed electrode method using batch and flow analysis (Sánchez‐Moreno et al. 2010), p-aminoacetophenone and phloroglucinol (Parmar et al. 2010), ultrasound-assisted cloud point extraction (UACPE) (Hashemi and Daryanavard 2012), electrospray ionization mass spectrometry using CYDTA (Hotta et al. 2012), HPLC and preconcentration by CPE with 1-(2-thiazolylazo)-2-naphthol (TAN) as the chelating agent (Wang et al. 2010), ytterbium (III) hydroxide (Duran et al. 2009), mixed-micelle cloud point extraction using electrothermal atomic absorption spectrometry (ET-AAS) (Ezoddin et al. 2010), room temperature ionic liquids (RTILs) for hollow fiber liquid phase microextraction (HF-LPME) combined with flame atomic absorption spectrometry (FAAS), etc., have been developed (Zeng et al. 2012).
It is evident from the literature that hexavalent chromium compounds are 10 to 100 times more toxic than trivalent chromium compounds when administered orally. The World Health Organization (WHO) and the European Community Directive (ECD) for drinking water has set the limit of total chromium not exceeding 50 μg L−1, while the maximum concentration criterion for Cr(VI) in freshwater is 16 μg L−1, sea water contains between 0.1 and 0.5 μg L−1 and unpolluted river water from 0.3 to 0.6 μg L−1. Since the concentration of chromium, mainly Cr(VI), is very low in many natural waters, a highly sensitive method is required for its speciation (Arancibia et al. 2012). Innumerable techniques and methods were reported for chromium speciation using highly sophisticated equipment. Among the plethora of the methods, photometric and fluorometric methods are comparatively simple and relatively sensitive. Hence, speciative determination of chromium by parameter selective approach using a novel thiourea derivative was proposed. This paper is an extension of the work carried out and formerly reported by the authors (Sunil and Rao 2015). Many analytical methods reported for chromium determination are based on the Beer's law and the metal ligand complexation studies by addition of oxidizing agents like hydrogen peroxide. But, the reaction utilized in the current study is a unique catalytic reaction in itself because the reagent synthesis is very simple and there is no need to add any oxidizing agent. There are no pre-concentration methods involved, the entire study can be done at normal room temperature, no inert atmosphere required, it is bench-stable and the methods are cost-effective.
Interference by foreign ions
In the speciative determination of chromium, the effect of associated metal ions and anions was studied. It was observed that metal ions like Na(I), Ba(II), Bi(III), Sb(III), V(V), W(VI), Ru(III) and Re(II) showed no interference even up to 1,500-folds. Other metal ions like Mn(II), Co(II), As(V), Pb(II), Hg(II), Cd(II), Zn(II), Pd(II), Ni(II), Zn(II), Ca(II), Mg(II), Zr(IV), Rh(III), Os(IV), Au(III), Mo(IV), Al(III), Ir(III), Pt(II) and Ag(I) do not interfere up to 800-folds at the pH of 8.0. Fe(II) and Cu(II) interfere up to 20-folds, which can be masked by the addition of tartarate and thiosulphate, respectively.
Analytical application of the method
Determination of chromium (III) species using the proposed and standard AAS methods
Amount of Cr (III) added (ng)
Experimental values for Cr (III) (ng) ( n = 3)
149.7 ± 0.04
149.4 ± 0.06
149.6 ± 0.06
132.8 ± 0.08
132.5 ± 0.07
132.3 ± 0.05
108.6 ± 0.04
108.9 ± 0.05
108.9 ± 0.07
Determination of chromium (VI) species using proposed and standard AAS methods
Amount of Cr (VI) added (ng)
Experimental values for Cr (VI) (ng) (n = 3)
179.4 ± 0.05
179.6 ± 0.08
179.5 ± 0.07
166.8 ± 0.08
166.5 ± 0.04
163.7 ± 0.05
138.4 ± 0.04
138.8 ± 0.05
138.5 ± 0.07
Statistical analysis of the obtained data for chromium (III) species
Statistical analysis of the obtained data for chromium (VI) species
Chemicals and instrumentation
Analytical grade chemicals with high purity purchased from Sigma-Aldrich Chemicals Ltd., Bengaluru, India, were used in the investigation. Similarly, HPLC-graded solvents purchased from Merck, Mumbai, Maharashtra, India, were used appropriately. The standard prescribed procedure was employed for the preparation of buffer solutions (Vogel 1961). The pH adjustments were appropriately done using Micropro pH meter (Techno Instruments Co., Bangalore, India). The instruments such as PerkinElmer LS-55 fluorimeter (PerkinElmer, Waltham, MA, USA) and Hitachi-2001 spectrophotometer (Hitachi Ltd, Chiyoda-ku, Japan) were utilized for experimental studies. Mettler Toledo AB204-S (Mettler-Toledo, LLC, Columbus, OH, USA) was utilized for weighing purposes.
In an ‘A’ grade 100-mL volumetric flask, 100.0361 mg of chromium (III) chloride was dissolved thoroughly and the resultant solution was standardised with EDTA. A stock solution of 6.3 mM (1.0 mg/mL) of chromium (III) was obtained.
In a 100-mL volumetric flask, 100.0704 mg of potassium dichromate was weighed, and deionised water was added up to the mark. The prepared solution was standardised by titrating with Mohr's salt, using diphenylamine as an indicator along with 2.0 mL of 1:1 H3PO4. A stock solution of 3.4 mM (1.0 mg/mL) of chromium (VI) was obtained.
1.0407 g of 1,10-phenanthroline was weighed and dissolved in ethanol in a 100-mL volumetric flask to get 0.58 mM of 1,10-phenanthroline reagent.
By weighing 1.0207 g of 2,2'-bipyridyl in a 100-mL volumetric flask, 0.66 mM of 2,2'-bipyridyl reagent was prepared, and ethanol was added up to the mark.
In distilled water using a 100-mL volumetric flask to get a 1% SDS solution, 1.0 g of SDS was weighed and dissolved. In a 100-mL volumetric flask, 1.0 g of CTAB was weighed and dissolved in distilled water to get 1% CTAB solution.
The above recommended experimental procedures were followed as described (Vogel 1961).
The reagent, HPTU, was synthesized (Sunil and Rao 2012a) and the analytical parameters, and their influence was studied systematically. A solution of 1.0 mL of acetate buffer of pH = 4.0 and appropriate amount (5 to 300 ng/mL) of chromium (III) solution was pipetted in to a 10.0-mL volumetric flask, followed by 1.0 mL of 1,10-phenanthroline and 1.0 mL of 1% SDS. The temperature was maintained at 25°C. Two milliliters of HPTU (1 mg/mL) solution was then added, and millipore water was added up to the mark. The resulting reaction mixture was transferred into 10-mm quartz cuvettes. The photometric measurements were recorded at λ Max = 416 nm. The fluorescence emission measurements were recorded at λ Em = 520 nm upon excitation at λ Ex = 416 nm, respectively, at 30 min. The blank experiments were repeated by following the same procedure to obtain relative fluorescence intensity I 0 and the value of I 0 /I was calculated. The calibration graph was plotted and the method was applied for the determination of chromium in waste water and plant samples. Water samples were boiled, treated with concentrated nitric acid and then filtered to remove organic particulate matter before using for the analysis. The digestion for plant sample was done as mentioned (Sunil and Rao 2012b). The same procedure was followed by taking chromium (VI) solution. Here, 2,2′-bipyridyl was used as an activator and 1% CTAB as a surfactant.
The results suggest that the speciative determination of chromium species was achieved by the selective application of parameters of pH, activators and surfactants using photometric and fluorometric techniques. Chromium(III) was determined in the pH range of 3.5 to 4.2 and in presence of 1,10-phenanthroline as an activator and SDS as a surfactant. Chromium(VI) was determined in the pH range of 7.8 to 8.4 and in presence of 2,2′-bipyridyl as an activator and CTAB as a surfactant. The methods are fairly sensitive with a determination range of 0.3 to 250 ng/mL. The proposed methods were applied to tap water, rain water and drainage water with satisfactory results.
Authors are thankful to the Founder Chancellor, Bhagawan Sri Sathya Sai Baba and the authorities of Sri Sathya Sai Institute of Higher Learning for the support and guidance.
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