Servicios
Descargas
Buscar
Idiomas
P. Completa
INVESTIGATION OF METALS RELEASED FROM IMPORTED COOKWARE COLLECTED FROM A LOCAL MARKET IN RIYADH, SAUDI ARABIA
Ibrahim Mohammed Alrajhi; Hajo Idriss
Ibrahim Mohammed Alrajhi; Hajo Idriss
INVESTIGATION OF METALS RELEASED FROM IMPORTED COOKWARE COLLECTED FROM A LOCAL MARKET IN RIYADH, SAUDI ARABIA
INVESTIGACIÓN SOBRE LA LIBERACIÓN DE METALES DE UTENSILIOS DE COCINA IMPORTADOS, RECOLECTADOS EN UN MERCADO LOCAL DE RIAD, ARABIA SAUDITA
Revista internacional de contaminación ambiental, vol. 37, 53561, 2021
Universidad Nacional Autónoma de México, Centro de Ciencias de la Atmósfera
resúmenes
secciones
referencias
imágenes

ABSTRACT: Monitoring the presence of heavy metals in cookware intended for use by both humans and animals is of interest, because of their toxic effects. In this report, a study has been conducted to determine the heavy metals released from 46 items of metallic cookware purchased from a local market in Riyadh. Mn, Fe, Cu, Cr, As, Zn, Ni, Al, Cd and Pb, were analyzed using an inductively coupled plasma-optical emission spectrometer. The order of concentration of essential and toxic elements in all samples showed the following trend: Mn > Al > Pb = As > Fe > Zn > Cu = Ni = Cd > Cr. This study highlighted the importance of the metal release monitoring from cooking utensils in order to protect people from the dangers posed by toxic metals.

Key words: ICP-OES, cookware, heavy metals.

RESUMEN: El monitoreo de la presencia de metales pesados en utensilios de cocina destinados a ser utilizados tanto por humanos como por animales es de interés debido a sus efectos tóxicos. En este informe se realizó un estudio para determinar los metales pesados liberados de 46 utensilios de cocina metálicos comprados en un mercado local en Riad. Se analizaron Mn, Fe, Cu, Cr, As, Zn, Ni, Al, Cd y Pb usando un espectrómetro de emisión de plasma óptico acoplado inductivamente. El orden de concentración de elementos esenciales y tóxicos en todas las muestras mostró la siguiente tendencia: Mn > Al > Pb = As > Fe > Zn > Cu = Ni = Cd > Cr. Esta investigación destacó la importancia del monitoreo de la liberación de metales de los utensilios de cocina para proteger a las personas de los peligros que representan los metales tóxicos.

Palabras clave: ICP-OES, utensilios de cocina metálicos, metales pesados.

Carátula del artículo

Articles

INVESTIGATION OF METALS RELEASED FROM IMPORTED COOKWARE COLLECTED FROM A LOCAL MARKET IN RIYADH, SAUDI ARABIA

INVESTIGACIÓN SOBRE LA LIBERACIÓN DE METALES DE UTENSILIOS DE COCINA IMPORTADOS, RECOLECTADOS EN UN MERCADO LOCAL DE RIAD, ARABIA SAUDITA

Ibrahim Mohammed Alrajhi
Prince Sultan Military Medical City, Kingdom of Saudi Arabia
Hajo Idriss
Al-Imam Mohamed Ibn Saud Islamic University, Saudi Arabia
Sudan Atomic Energy Commission, Sudan
Revista internacional de contaminación ambiental, vol. 37, 53561, 2021
Universidad Nacional Autónoma de México, Centro de Ciencias de la Atmósfera

Received: 01 March 2019

Accepted: 01 March 2020

INTRODUCTION

People have, over a period of time that predates historical record, constantly ground and stewed foods using various grinding techniques and cook- ware (Street et al. 2020). These varied in type and sophistication by both geographical location and technological means. The customs and traditions of the society have significantly contributed to the shape and functionality of the utensils and equipment that were used in the milling and cooking processes, as have the culture, level of urbanization and typical life- style. Food contamination by heavy metals is a prevalent concern in public health, as food is the principal source of nutrition for humans (Pennington. 2000, Jigam et al. 2011). Zinc is relatively harmless. Only exposure to high doses has toxic effects, making acute zinc intoxication a rare event (Plum et al. 2010). Copper surfeit can affect different organ systems leading to diseases such as diabetes, cardiovascular system illnesses, Alzheimer disease, angiogenesis, and some forms of cancer (Finney et al. 2009). Nickel contact can cause a variety of side effects on human health, such as allergy, cardiovascular and kidney diseases and lung fibrosis, (Genchi et al. 2020). The toxicity of Al to humans is mainly related to neurotoxicity and the development of neurodegenerative diseases (Verstraeten et al. 2008). Lead may disturb physiological functions and induce numerous adverse effects such as chronic obstructive pulmonary disease, asthma, lung cancer and cardiovascular diseases (Boskabady et al. 2018). Chromium (Cr) usually exists in the environment in different multi oxidation states. Cr (VI) has toxic, genotoxic, mutagenic and carcino- genic effects, causing skin lesions, ulceration, nasal septum and lung carcinoma (Yoshinaga et al. 2018). Chronic ingestion of arsenic has been associated with various health effects including skin lesions, diabetes mellitus, bronchitis, cardiovascular disease, and hae- matological effects (Sinha and Prasad 2020). Over exposure to cadmium can lead may cause lung, liver, skeletal and renal problems, and cancer (Djordjevic et al. 2019). Continuous exposure to manganese can lead to Parkinson’s disease (Hernández-Pellón et al. 2017). Nowadays, awareness about food safety is increasing in most parts of the world. Many of the heavy metals are probably the most harmful and insidious contaminants because of their biological non-degradable nature and their potential to cause adverse effects in human beings, at a certain level of exposure and absorption (Alabdula’aly et al. 2009). Therefore, monitoring the presence of heavy metals in metallic cookware intended for use by both humans and animals is of interest and requires particular at- tention, because of their toxic effects. The overall objective of this work is to build up a nation-wide baseline data regarding heavy metals as well as concentration in metallic cookware in Saudi Arabia This study aims to determine the metal released from a variety of common cookware, purchased from Riyadh local market.

MATERIALS AND METHODS
Sample collection and preparation

A total of 46 different types of samples of metallic (aluminium) cookware for human use were collected from the local market of Riyadh city and transported to the environmental research laboratory at Al-Imam Mohammad Ibn Saud Islamic University for elemental analysis. The aluminium pots were firstly washed with distilled water many times to remove any possible contamination. Afterward, 0.9. liters of distilled water were added to the aluminium cookware pots, then allowed to boil for 30 minutes at 100 ºC in order to allow prolonged contact to take place between the distilled water and the cookware wall, finally, 15 mL of the remaining water was taken for elemental analysis.

Chemicals and reagents

All the standard stock solutions of heavy metals were certified reference materials that were purchased from Agilent Technologies (USA). HNO3 and H2O2 were heavy metal analysis grade and purchased from Wako Chemical Co. (USA). Reagent water, toluene, and acetone were of analytical reagent grade purchased from J.T. Baker (USA).

Spectrometric analysis

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 was purged with argon. The purge rate during normal operation is 0.5 L/min. To enable the method, intelligent calibration logic (ICAL) transfer between individual instruments, 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 the 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. ICP-OES determinations of elements concentration were performed using the emission lines 228.802, 267.716, 324.752, 238.204, 285.213, 259.372, 231.604, 220.353, 213.857, 189.641, 196.090, 384.401 and 311.071 λ (nm) for the elements Cd, Cr, Cu, Fe, Mn, Ni, Pb, Zn, As and Al respectively.

Quality control

An adequate quality control method and vigilance were carried out in order to get reliable results. Throughout the experiments, all glass ware and equipment were cautiously washed beginning with acetone followed by 5 % HNO3 and ending with repeated rinsing distilled water to prevent contamination. Reagent blank determinations were used to correct the readings. The lower detection limit values of the elements were found to be 0.001 mg/L for Cr, 0.001 mg/L for Cu, 0.0001 mg/L for Zn, 0.002 mg/L for Fe, 0.0001 mg/L for Mn, 0.0001 mg/L for Cd, 0.001 mg/L for Al, 0.001 mg/L for Ni, 0.01 mg/L for Se, 0.004 for Pb and 0.01 mg/L for As in this study. Samples were measured tow time and 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 for quantitative sample results.

RESULTS AND DISCUSSION

Determination of metals released from imported cookware is very important, since several elements play major roles in various metabolic processes in the human body. Moreover, some of these elements are toxic if consumed in excessive quantities (Baran et al. 2019). In this study, 10 elements (i.e. Mn, Fe, Cu, Cr, Zn, Ni, Al, Pb, As and Cd) in 46 items of cookware collected from a local market in Riyadh were investigated using an inductively coupled plasma-optical emission spectrometer (ICP-OES), as shown in (Table I and Table II).

TABLE I
STATISTICAL SUMMARY OF Cd, Cr, Cu, Fe AND Mn CONCENTRATION RELEASED FROM IMPORTED METALLIC COOKWARE (mg/L).

Where: LDL = Lower than detection limit, Min = Minimum, Max = Maximum, Avg = Average and Std = Standard deviation.

TABLE II
STATISTICAL SUMMARY OF Ni, Zn, Al, Pb AND As CONCENTRATION RELEASED FROM IMPORTED METALLIC COOKWARE (mg/L).

Where: LDL = Lower than detection limit, Min = Minimum, Max = Maximum, Avg = Average and Std = Standard deviation.

Iron was detected in all measured samples and ranged from 0.002 to 0.574 mg/L and an average value of 0.057 mg/L. Iron is an important element for human beings and animals (Shukla et al. 2018), and is an essential component of hemoglobin (Balarabe et al. 2019). It facilitates the oxidation of carbohydrates, proteins and fats to control body weight, which is an extremely important factor in diabetes; furthermore, an iron deficiency can induce anaemia (Zhang et al. 2018).

Manganese is essential in many biological pro- cesses such as, blood sugar regulation and bone growth, as well as being a cellular antioxidant (Pfalzer and Bowman 2017). Manganese was detected in 91.30 % of the samples, within a range of 0.001 to 0.505 mg/L, with an average value of 0.073 mg/L. Cu was detected in 97.82 % of the samples and found to be in the range of 0.001 to 0.175 mg/L, with an average value of 0.014 mg/L. Copper has numerous functions in the human body, and they are essential nutrients that play important roles in the pro- duction of hemoglobin for human health; however, an excessive intake of copper has been reported to be toxic (Ahmed et al. 2005).

Chromium is important to make use of glucose as reported by Yagi et al. (2013). Chromium was detected in 67.39 % of the samples, The Cr concentration varied from 0.001 to 0.017 mg/L, with an average value of 0.002 mg/L.

Cadmium was detected in 10.86 % of the 46 samples. Cadmium is an extremely toxic metal found naturally in the soil, but also spread in the environment due to human activity. Over exposure to cadmium can lead to lung, liver, skeletal and renal problems and cancer (Djordjevic et al. 2019).

Zinc was detected in 76.08 % of the samples and the concentrations varied from 0.03 to 0.017 mg/L with an average value of 0.001 mg/L. Zinc has essential function in carbohydrate and cholesterol metabolism (Ahmed et al. 2005). Acute zinc poison- ing is a rare event, except in very high doses (Plum et al.2010).

Nickel was detected in 63.043 % of the samples and the concentrations varied from 0.002 to 0.213 mg/L with an average value of 0.007 mg/L. Trace amounts of nickel may be beneficial as an activator of some enzyme systems, but its toxicity at higher levels is more prominent (Fangkun 2011).

The arsenic content of the samples was detected in 69.56 % of the samples and found to be in the range from 0.012 to 0.505 mg/L with an average value of 0.073 mg/L.Arsenic is a naturally occurring element that can be toxic to humans, animals and plants; however, its toxicity varies, depending on what form it is (Hare et al. 2019).

Aluminum concentration was analyzed in all samples and ranged from 0.01 to 0.175 mg/L, with an average of 0.014 mg/L. The toxicity of Al to humans is mainly related to neurotoxicity and the development of neurodegenerative diseases (Chris- topher 2012). Lead was detected in 69.56 % of the samples. Its concentration ranged from 0.099 to 0.574 mg/L with an average of 0.057 mg/L. Lead is a naturally occurring element, and is a common industrial metal that has become widespread. Lead contamination varies and manifests itself in other ways than in green plants (Ahmad et al. 2019). Lead has severe health effects even at relatively low levels in the body, and can cross the placenta and damage developing foetal nervous systems (Khan and Khan 2017). Lead causes both acute and chronic poisoning; it has adverse effects on the kidneys, liver, heart and both the vascular and immune systems (Zhang 2001).

CONCLUSIONS

The elemental measurement for metallic cook- ware is very important from the perspective of food safety. The average concentrations of measured Ni, Zn, Al, Pb, As, Cd, Cr,Cu, Fe and Mn released from metallic cookware are comparatively normal. This implies that the metallic cookware under investiga- tion are free of metals contamination and without possibility of metallic poisoning. The outcome of this work highlights the concept of safety for food security by analyzing with the highest quality standards the metallic cookware and, thus, expanding public awareness.

Supplementary material
REFERENCES
Alabdula’aly A. I. and Khan M. A. (2009). Heavy metals in cooler waters in Riyadh, Saudi Arabia. Environ. Monit. Assess. 157 (1-4), 23-28. https://doi.org/10.1007/s10661-008-0511-3
Ahmad I., Khan B., Asad N., Mian I. A. and Jamil M. (2019). Traffic-related lead pollution in roadside soils and plants in Khyber Pakhtunkhwa, Pakistan: implications for human health. International Journal of Environmental Science and Technology. 16 (12), 8015-8022. https://doi.org/10.1007/s13762-019-02216-7
Akinbile C. O. and Haque A. M. M (2012). Arsenic contamination in irrigation water for rice production in Bangladesh: A Review. Trends in Applied Sciences Research 7, 331-349. https://doi.org/10.3923/tasr.2012.331.349
Anderson R. A., Bryden N. A. and Polansky M. M. (1992). Dietary chromium intake. Trace Elem. Res. 32 (1-3), 117-121. https://doi.org/10.1007/BF02784595
Balarabe M. A. and Folashade A. Z. (2019). Determina- tion of iron in some selected iron containing tablets using redox titration. World Journal of Applied Chemistry. 4 (3), 42-44. https://doi.org/10.11648/j.wjac.20190403.13
Baran A., Mierzwa-Hersztek M., Gondek K., Tarnawski M., Szara M., Gorczyca O. and Koniarz T. (2019). The influence of the quantity and quality of sediment organic matter on the potential mobility and toxicity of trace elements in bottom sediment. Environ. Geochem. Health. 41, 2893-2910. https://doi.org/10.1007/s10653-019-00359-7
Boskabady M., Marefati N., Farkhondeh T., Shakeri F., Farshbaf A. and Boskabady M. H. (2018). The effect of environmental lead exposure on human health and the contribution of inflammatory mechanisms, a review. Environ. Int. 120, 404-420. https://doi.org/10.1016/j.envint.2018.08.013
Choi H. S. and Choi H. S. (2020). Relationships of lead, mercury and cadmium levels with the timing of men- arche among Korean girls. Child. Health. Nurs. Res. 26 (1), 98-106. https://doi.org/10.4094/chnr.2020.26.1.98
Djordjevic V.R., Wallace D.R., Schweitzer A., Boricic N., Knezevic D., Matic S., Grubor N., Kerkez M., Radenkovic D., Bulat Z. and Antonijevic B. (2019). Environmental cadmium exposure and pancreatic cancer: Evidence from case control, animal and in vitro studies. Environ. Int. 128, 353-361. https://doi.org/10.1016/j.envint.2019.04.048
Finney L., Vogt S., Fukai T. and Glesne D. (2009). Copper and angiogenesis: unravelling a relationship key to cancer progression. Clin. Exp. Pharmacol. Physiol.36 (1), 88-94. https://doi.org/10.1111/j.1440-1681.2008.04969.x
Genchi G., Carocci A., Lauria G., Sinicropi M. S. and Catalano A. (2020). Nickel: human health and environ- mental toxicology. Int. J. Environ. Res. Public .Health. 17 (3), 679. https://doi.org/10.3390/ijerph17030679
Hare V., Chowdhary P., Kumar B., Sharma D. C. and Baghel V. S. (2019). Arsenic toxicity and its remediation strategies for fighting the environmental threat. In Emerging and eco-friendly approaches for waste management. 143-170. https://doi.org/10.1007/978-981-10-8669-4_8
Hernández-Pellón A., Fernández-Olmo I., Ledoux F., Courcot L. and Courcot D. (2017). Characterization of manganese-bearing particles in the vicinities of a manganese alloy plant. Chemosphere 175, 411-424. https://doi.org/10.1016/j.chemosphere.2017.02.056
Jigam A. A., Dauda B. E., Jimoh T., Yusuf H. N. and Umar Z. T. (2011). Determination of copper, zinc, lead and some biochemical parameters in fresh cow milk from different locations in Niger State, Nigeria. Afr. J. Food. Sci. 5, 156-60.
Khan S. and Khan R. A. (2017). Chronic stress leads to anxiety and depression. Ann Psychiatry Ment Health 5 (1), 1091
Malaekeh S. M. A., Farhadiannezhad M., Afshari H. and Hossien O. (2019). Effect dusts phenomena on health. Indian Journal of Forensic Medicine and Toxicology 13 (2), 373-377.
Yoshinaga M., Ninomiya H., Al Hossain M. A., Sudo M., Akhand A. A., Ahsan N., M Abdul-Alim., Khalequz- zama M., Iida M., Yajima I., Ohgami N., Kato M. (2018). A comprehensive study including monitoring, assessment of health effects and development of a remediation method for chromium pollution. Chemosphere 201, 667-675. https://doi.org/10.1016/j.chemosphere.2018.03.026
Pennington J. A. (2000). Total diet studies - experiences in the United States. J. Food Composit. Analysis. 13, 539-544. https://doi.org/10.1006/jfca.2000.0905
Pfalzer A.C. and Bowman A.B. (2017). Relationships between essential manganese biology and manganese toxicity in neurological disease. Curr. Envir. Health. Rpt. 4, 223-228. https://doi.org/10.1007/s40572-017-0136-1
Plum L. M., Rink L. and Haase H. (2010). The essential toxin: impact of zinc on human health. Int. J. Environ. Res. Public. Health. 7 (4), 1342-1365. https://doi.org/10.3390/ijerph7041342
Salama A. K. and Radwan M. A. (2005). Heavy metals (Cd, Pb) and trace elements (Cu, Zn) contents in some foodstuffs from the Egyptian market. Emir. J. Agric. Sci. 17 (1), 34-42. https://doi.org/10.9755/ejfa. v12i1.5046
Shukla A. K., Behera S. K., Pakhre A. and Chaudhari S. K. (2018). Micronutrients in soils, plants, animals and humans. Indian Journal of Fertilisers.14 (3), 30-54.
Sinha D. and Prasad P. (2020). Health effects inflicted by chronic low level arsenic contamination in groundwater: A global public health challenge. J. Appl. Toxicol. 40 (1), 87-131. https://doi.org/10.1002/jat.3823
Street R. A., Mathee A., Tanda S., Hauzenberger C., Naidoo S. and Goessler W. (2020). Recycling of scrap metal into artisanal cookware in the informal sector: A public health threat from multi metal exposure in South Africa. Sci. Total Environ. 699, 134324. https://doi.org/10.1016/j.scitotenv.2019.134324
Verstraeten S. V., Aimo L. and Oteiza P. I. (2008). Aluminium and lead: molecular mechanisms of brain toxicity. Arch Toxicol. 82 (11), 789-802. https://doi.org/10.1007/s00204-008-0345-3
Yagi S., Rahman A. E. A., Elhassan G. O. and Mohammed A. M. (2013). Elemental analysis of ten Sudanese medicinal plants using X-ray fluorescence. Journal of Applied and Industrial Sciences.1 (1), 49-53.
Yu B., Zhang Y., Shukla A., Shukla S. S. and Dorris K. L. (2001).The removal of heavy metals from aqueous solutions by sawdust adsorption removal of lead and comparison of its adsorption with copper. J. Hazard. Mater. 84 (1), 83-94 https://doi.org/10.1016/S0304-3894(01)00198-4
Zhang R., Sung S. H., Feng G., Zhang C. J., Tang B. Z. and Liu B. (2018). Aggregation-induced emission probe for specific turn-on quantification of soluble transferrin receptor: an important disease marker for iron deficiency anemia and kidney diseases. Anal. Chem. 90 (2), 1154-1160. https://doi.org/10.1021/acs.analchem.7b03694
Zhuang P., Huiling Z. O. U. and Wensheng S. H. U. (2009). Biotransfer of heavy metals along a soil-plant- insect-chicken food chain: Field study. J. Environ. Sci. (China). 21 (6), 849-853. https://doi.org/10.1016/S1001-0742(08)62351-7
Zhu F., Fan W., Wang X., Qu L. and Yao S. (2011). Health risk assessment of eight heavy metals in nine varieties of edible vegetable oils consumed in China. Food. Chem. Toxicol. 49 (12), 3081-3085. https://doi.org/10.1016/j.fct.2011.09.019
Notes
Author notes

* Author for correspondence: hjoidriss@gmail.com

TABLE I
STATISTICAL SUMMARY OF Cd, Cr, Cu, Fe AND Mn CONCENTRATION RELEASED FROM IMPORTED METALLIC COOKWARE (mg/L).

Where: LDL = Lower than detection limit, Min = Minimum, Max = Maximum, Avg = Average and Std = Standard deviation.
TABLE II
STATISTICAL SUMMARY OF Ni, Zn, Al, Pb AND As CONCENTRATION RELEASED FROM IMPORTED METALLIC COOKWARE (mg/L).

Where: LDL = Lower than detection limit, Min = Minimum, Max = Maximum, Avg = Average and Std = Standard deviation.
Buscar:
Contexto
Descargar
Todas
Imágenes
Scientific article viewer generated from XML JATS4R by Redalyc