Journal of Analytical Sciences, Methods and Instrumentation
Vol.4 No.2(2014), Article ID:46619,3 pages DOI:10.4236/jasmi.2014.42007

Measurement of Different Types of Potato Chips by Inductively Coupled Plasma-Optical Emission Spectrometer

AL-rajhi, M.A.

Physics Department, College of Science, Al Imam Mohammad Ibn Saud Islamic University, Riyadh, KSA

Email: rajhi.mai9@gmail.com

Copyright © 2014 by author and Scientific Research Publishing Inc.

This work is licensed under the Creative Commons Attribution International License (CC BY).

http://creativecommons.org/licenses/by/4.0/

Received 18 March 2014; revised 18 April 2014; accepted 25 April 2014

ABSTRACT

Potato chips are considered as one of the most popular and preferable children’s foods in Saudi Arabia. The aim of this study was to examine the concentration of 12 chemical elements (i.e. Cd, Cr, Cu, Fe, Mg, Mn, Ni, Pb, Zn, As, Se and Al) in different types of potato chips. Samples were analyzed using an Inductively Coupled Plasma-Optical Emission Spectrometer (ICP-OES). The average concentrations of analyzed elements in all potato chips were examined and compared with the recommendations of international organizations concerned with food safety. From the human health point of view, this investigation showed that there was no possible health risk to consumers due to the intake of potato chips.

Keywords:ICPl-OES, Potato Chips, Heavy and Essential Elements

1. Introduction

Inductively Coupled Plasma-Optical Emission Spectrometer is an analytical instrument used for the detection of metals in different environmental samples. It is a type of emission spectroscopy that uses the inductively coupled plasma to produce excited atoms and ions that emit electromagnetic radiation at wavelengths characteristic of a particular element. One of the advantages of inductively coupled plasma optical emission spectrometry (ICP-OES) as an analytical technique is that major, minor and trace element determinations can be performed simultaneously, thus minimizing sample handling and reducing sample contamination [1] . The concentration level of metals in foods are very importance due to the significant role of metal ions in health and diseases which include the requirement for intake of essential trace elements to the toxicity associated with high concentration of metals [2] . Some metals are important to human health (i.e. Fe, Se, Zn, and Cr), though they are potentially harmful if consumed in large quantities. Heavy metals like (Cd, As Pb) are most serious contaminants for environment and human beings [3] . Once excessive significant metals enter in the soil, water or air, it’s going to cause hazards to human health through consumption of food crops and vegetables cultivated in these contaminated environments. Some metals are important to human health (i.e. Fe, Se, Zn, and Cr), although they are potentially harmful if consumed in large quantities. Heavy metals such as (Cd, As Pb) are the most dangerous contaminants for environment and human beings 2. Once excessive heavy metals enter in the soil, water or air, it may cause hazards to human health through consumption of food crops and vegetables cultivated in these contaminated environments [4] . Ingestion of contaminated food is one of the main routes through which heavy metals enter the human body [5] . Contamination of food can occur at any point in the production chain (i.e. from the raw materials, processing, packing, transportation, storage or marketing to consumption. Because of improper subject to contamination by microorganism, metals as well as pesticides. Obviously, data on the concentrations of metals in food items at the point of consumption are necessary for estimation human exposure to metals [6] . The toxicity of heavy metals might be by the displacement of physiologically applicable metal Cd can replace Cu and Fe in cytoplasmic and membrane proteins. Especially in the form of divalent, the free metal ions can support the generation of ultra-oxide and hydroxyl radical which, in turn, can lead to deterioration of lipids, nucleic acids and proteins [7] . The current study makes an attempt to measure the concentration of Cd, Cr, Cu, Fe, K, Mg, Mn, Ni, Pb, Zn, As, Se, Al and V in potato chips by using ICP-OES.

2. Material and Method

2.1. Study Area

The study area is Riyadh City, the capital city of the Kingdom of Saudi Arabia with an area of about 1554 km². It is located centrally in the Najd region and lies between latitude 34˚ - 38˚ north and longitude 43˚ - 46˚ east (Figure 1).

2.2. Sample Collection

A total of 13 types of potato chips were collected from the supermarkets around the city of Riyadh and transported in plastic bags to the Environmental Research Laboratory at Al Imam Mahammad Ibn Saud Islamic University for elemental analysis. Samples were dried, and after drying, samples were grained into a fine powder using a ceramic mill and stored in polyethylene bags until used for acid digestion.

Figure 1. Kingdom of Saudi Arabia map showing the study area.

2.3. Sample Preparation

10 ml, high purity HNO3 and 2 ml H2O2 were added to the beaker containing 2 g of dry samples placed in the fume cupboard for two days for digestion. The mixture was then digested at 80˚C till the transparent solution was achieved. After cooling, the digested samples were filtered using Buchner funnels and the filtrate was diluted to 50 ml with distill water. The final solution were used for the elements analysis namely Cd, Cr, Cu, Fe, K, Mg, Mn, Ni, Pb, Zn, As, Se and Al by ICP optical emission spectrometer. The recovery values were nearly quantitative (95%) for digestion method. The relative standard deviations were less than 10% for all investigated elements.

2.4. Samples Measurement

The measurements were performed using a GENESIS ICP optical emission spectrometer (SPECTRO Analytical Instruments, Kleve, Germany) with axial plasma observation. The instrument includes a Paschen-Runge mount spectrometer, constructed employing the Optimized Rowland Circle Alignment (ORCA) technique. It consists of two hollow section cast shells, designed for direct thermal stabilization and small volume. 15 pre-aligned linear CCD detectors are installed on the outside of the optics body, which allow fast, simultaneous spectrum capture of the wavelength range between 175 nm and 777 nm. For UV access (<200 nm), the optical system purged with argon. The purge rate during normal operation is 0.5 L/min. To enable method transfer between individual instruments, ICAL (Intelligent Calibration Logic) was used to normalize the wavelength and the intensity scale of the optical system to a reference optic (“optic master”). Stability of the forward power in the case of rapidly changing sample loads was achieved through use of an air-cooled ICP-generator, based on a free running 27.12 MHz system. All ICP operating parameters were software controlled. The ICP-OES instrument was initialized and allowed to achieve thermal equilibrium over 30 min. Multi-element Solution Standards obtained from Agilent technology were used to calibrate and quantitative sample results. The lower detection limit values of the elements were found to be 0.001 mg/kg for Cr, 0.001 mg/kg for Cu, 0.0001 mg/kg for Zn, 0.002 mg/kg for Fe, 0.003 mg/kg for V, 0.0001 mg/kg for Mn, 0.0001 mg/kg for Cd, 0.001 mg/kg for Al, 0.001 mg/kg for Ni, 0.01 mg/kg for Se, 0.004 for Pb and 0.01 mg/kg for As in this study.

2.5. Quality Assurance

Appropriate quality assurance procedures and precautions were carried out to ensure the reliability of the results. During the experiments, all glass wares and equipments were carefully cleaned starting with 5% HNO3 and ending with repeated rinsing distilled water to prevent contamination. Reagent blank determinations were used to correct the instrument readings. The lower detection limit values of the elements were found to be 0.001 mg/kg for Cr, 0.001 mg/kg for Cu, 0.0001 mg/kg for Zn, 0.002 mg/kg for Fe, 0.003 mg/kg for V, 0.0001 mg/kg for Mn, 0.0001 mg/kg for Cd, 0.001 mg/kg for Al, 0.001 mg/kg for Ni, 0.01 mg/kg for Se, 0.004 for Pb and 0.01 mg/kg for As in this study. The recovery values were nearly quantitative (95%) for digestion method. The relative standard deviations were less than 10% for all investigated elements. Multi-element Solution Standards obtained from Agilent technology were used to calibrate and quantitative sample results.

3. Result and Discussion

Despite the remarkable improvement in the provision of healthy foods all over the world in recent decades, the prevalence of food contamination is still a source of concern in terms of health and economic consequences. For this reason, the present study aimed to analyze the heavy metals in different types of potato chips taken from the local markets in the capital of Saudi Arabia. The concentrations of essential elements in potato chips collected from different local markets of Riyadh are presented in Table1 On average, the values obtained were 0.0001 mg/kg for Cu, 0.0005 mg/kg for Fe, 0.0029 mg/kg for Mn, 0.0162 mg/kg for Ni, 0.0039 mg/kg for Zn, 0.0009 mg/kg for Cr and 0.0200 mg/kg for Se. The results indicate that the order of concentrations of essential elements in potato chips showed the following trend: Se > Ni > Zn > Mn > Cr> Fe > Cu. Comparing the results with the limits permitted by the World Health Organization and the Food and Agriculture Organization, it was found that the average concentrations of the obtained results for Ni, Zn, Mn, Se, Cr, Fe and Cu were below the legal limits. This implies that chemical contamination was not present for any of the elements mentioned [8] -[10] . In contrast, some metals (e.g. Cu, Zn, Fe, Mn, Cretc.) are needed in the body in very small amounts (i.e. less than 100 mg/kg) (Grivetti, 2000). It is important to evaluate the concentration of heavy metals in potato chips to report possible contamination that would represent a health hazard. The concentrations of heavy metals Cd, Al, Pb and As are presented in Table2 The concentrations of Cd, Al, Pb and As ranged from 0.0001 - 0.0006 mg/kg, 0.0025 - 0.0114 mg/kg, 0.0014 - 0.0062 mg/kg and 0.0105 - 0.0712 mg/kg, respectively. On average, the values obtained were 0.0001 mg/kg for Cd, 0.0056 mg/ kg for Al, 0.0026 mg/kg for Pb and 0.0212 mg/kg for As. From the results of heavy metal measurements, the order of concentrations in potato chips showed the following trend: As > Al > Pb > Cd. Heavy metals can be very harmful even at low concentrations when ingested over a long time period [11] [12] . According to the World Health Organization’s and Food and Agriculture Organization’s permissible limits of heavy metal in foodstuffs, obviously the average concentrations of As, Al, Pb and Cd fall far

Table 1 . Concentration and statistical summary of Cu, Fe, Mn, Ni, Zn, Se and Cr in potato chips samples.

Table 2. Concentration and statistical summary of Cd, Al, Pb and As in potato chips samples.

below the allowable limit [13] . The regression analysis showed that a significant correlation was noted between Ni and Zn (Figure 2), Ni and Mn (Figure 3), Mn and Fe (Figure 4) and Se and As (Figure 5), and a positive correlation was reported between Se and Pb, as shown in Figure 6.

Figure 2. Ni concentration as function of Z concentration.

Figure 3. Mn concentration as function of Ni concentration.

Figure 4. Fe concentration as function of Mn concentration.

Figure 5. Se concentration as function of As concentration.

Figure 6. As concentration as function of Pb concentration.

4. Conclusions

From measurements of trace element and heavy metal concentration in potato chips purchased from the local market of Riyadh city. To sum up, the following conclusions can be drawn:

• No contamination have been observed in all samples analyzed;

• The essential elements concentration found to be in good level;

• The heavy metal concentration element concentration found to be within the acceptable recommended standard level given by FAO and WHO.

Acknowledgments

The author would like to thank many colleagues at AL imam Mohammad Ibn Saud Islamic University for their valuable help with these experiments.

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