بررسی فلزهای سنگین در خاک برخی از شالیزارهای اطراف اصفهان و تاثیر کادمیم بر امنیت غذایی

نوع مقاله : مقاله پژوهشی

نویسندگان

بخش تحقیقات خاک و آب، مرکز تحقیقات و آموزش کشاورزی و منابع طبیعی استان اصفهان، سازمان تحقیقات، آموزش و ترویج کشاورزی، اصفهان، ایران

10.22059/ijswr.2024.379643.669760

چکیده

فلزهای سنگین می‌توانند سبب مشکلات مهم آلودگی محیطی و سلامت شوند. آلوده بودن برنج به کادمیم خطر جدی برای کیفیت و امنیت این محصول به شمار می‌رود. این پژوهش با هدف بررسی احتمال آلودگی خاک و دانه برنج برخی از شالیزارهای اطراف اصفهان به فلزهای سنگین انجام شد. به منظور انجام این پژوهش تعداد 105 نمونه خاک از 6 منطقه برنج‌کاری استان اصفهان برداشت و غلظت فلزهای سنگین روی، مس، آهن، کادمیم و سرب در نمونه‌ها اندازه‌گیری شد. برای تعیین آلودگی خاک به فلزهای سنگین از فاکتور آلودگی (CF) استفاده شد. غلظت کادمیم در ریشه، ساقه و دانه برنج اندازه‌گیری و شاخص‌های ضریب خطر (HQ)، فاکتور تجمع زیستی (BAF) و فاکتور انتقال (TF) کادمیم محاسبه گردید. نتایج نشان داد که غلظت فلزهایسنگین مس، روی و سرب از حد مجاز ارائه شده توسط سازمان محیط‌زیست کشور برای خاک‌های کشاورزی کم‌تر بود، درحالی‌که غلظت کادمیم در حدود 21 درصد از نمونه‌ها بیش‌تر از حد مجاز سازمان محیط‌زیست به‌دست آمد. روند CF فلزهای سنگین در نمونه‌های خاک به صورت CF-Cd>CF-Fe>CF-Pb>CF-Cu>CF-Zn مشاهده شد. میزان کادمیم در 4/36 درصد از نمونه‌های دانه‌ برنج کم‌تر از حد استاندارد ملی 12968 بود. مقدار HQ برای گروه بزرگسالان و کودکان به ترتیب در 5/54 و 2/18 درصد از مناطق مورد مطالعه کم‌تر از حد مجاز برای شاخص سلامت (1= HQ) به‌دست آمد. میانگین BAF 03/0 محاسبه شد. بر اساس نتایج BAF، کادمیم در دانه برنج تجمع پیدا نمی‌کند، اما باتوجه به مقادیر ضریب خطر، می‌تواند در آینده‌ای نزدیک سلامت هر دو گروه بزرگسالان و به‌طور ویژه کودکان را تهدید کند.

کلیدواژه‌ها

موضوعات


عنوان مقاله [English]

Investigation of heavy metals in the soil of some paddy fields around Isfahan and the effect of cadmium on food security

نویسندگان [English]

  • Hamid Reza Rahmani
  • Zahra Khanmohammadi
Departments of Soil and Water Research, Isfahan Agricultural and Natural Resources Research and Training Center, AREEO, Isfahan, Iran
چکیده [English]

ABSTRACT: Important environmental and health problems can be caused by heavy metals. Contamination of rice with cadmium is a serious risk for the quality and safety of this product. The objective of this study was to investigate the possibility of soil and rice grain contamination of some paddy fields of Isfahan Provence with heavy metals. A number of 105 soil samples were collected from 6 rice growing areas and the concentration of zinc, copper, iron, cadmium, and lead was measured. Contamination factor (CF) was used to determine soil contamination with heavy metals. Cadmium concentration was measured in the root, stem and grain of rice. The indices of hazard coefficient (HQ), bioaccumulation factor (BAF), and translocation factor (TF) of cadmium were calculated. The concentration of copper, zinc, and lead in the studied stations was lower than the permissible limit provided by the Iranian Environmental Organization for agricultural soils while the concentration of cadmium was higher than the permissible limit in about 21% of the studied samples. The trend of CF-Cd>CF-Fe>CF-Pb>CF-Cu>CF-Zn was observed. The rice grain cadmium concentration was lower than the national standard number 12968 in 36.4% of the samples. The value of HQ for adults and children was less than the permissible limit (HQ=1) in 54.5% and 18.2% of the studied samples, respectively. The average BAF was calculated as 0.03. According to the results, cadmium does not accumulate in the rice grain, but, it can threaten the health of both groups of adults and especially children in the near future.

کلیدواژه‌ها [English]

  • Bioaccumulation
  • contamination factor
  • hazard coefficient
  • heavy metals
  • rice

EXTENDED ABSTRACT

 

Introduction

Important environmental and health problems can be caused by heavy metals Heavy metals cannot be broken down into less harmful compounds due to chemical and biological processes. Therefore, they accumulate in soil and plants. Human health is directly affected by consuming crops grown in contaminated soils. Contamination of rice with cadmium is a serious risk for the quality and safety of this product.

Purpose

The objective of this study was to investigate the possibility of soil and rice grain contamination of some paddy fields of Isfahan Provence with heavy metals.

Research method

A number of 105 soil samples were collected from 6 rice growing areas and the concentration of zinc, copper, iron, cadmium, and lead were measured in the samples. Contamination factor (CF) was used to determine soil contamination with heavy metals. Cadmium concentration was measured in the root, stem and grain of rice. Estimated daily intake (EDI) and reference value of cadmium were used to calculate the non-cancerous hazard coefficient of cadmium (HQ). The indices of bioaccumulation factor (BAF), and translocation factor (TF) of cadmium were calculated.

Results

The concentration of copper, zinc, and lead in the studied stations was lower than the permissible limit provided by the Iranian Environmental Organization for agricultural soils while the concentration of cadmium was higher than the permissible limit in about 21% of the studied samples. The lowest lead contamination factor (CF-Pb) with a value of 0.32 was related to Qaleh Qasim station and the highest CF-Pb (2.15) was related to Jozdan station. The highest amount of CF-Cd was obtained in Jozdan station (1.75) and the lowest amount (0.96) was obtained in Chamgardan station. The trend of CF was observed as CF-Cd>CF-Fe>CF-Pb>CF-Cu>CF-Zn. The results showed that 11.4% of the CF-Cd values were in the low pollution class and 88.6% were in the medium pollution class. The amount of enrichment factor (EF) for heavy metals was obtained in the following order: cadmium > copper = iron > lead > zinc. The highest value of the enrichment factor for Cd was equal to 1.34 and the lowest value for Zn was equal to 1.02. The lowest amount of cadmium in rice grain was 0.24 mg kg-1 and the highest amount was 0.29 mg kg-1. The amount of the rice grain cadmium was lower than the national standard number 12968 in 36.4% of the samples. The amount estimated daily intake of cadmium through rice consumption (EDI) for adults ranged from 0.013 to 0.159 mg/kg/day, while for children it was in the range of 0.037 to 0.464 mg/kg/day. The value HQ for adults and children was less than the permissible limit of health index (HQ=1) in 54.5% and 18.2% of the studied samples, respectively. The lowest amount of HQ was related to the adults group (0.25) and the highest amount was 7.73 related to the children group. The amount of bioaccumulation factor of cadmium for rice grain was in the range of 0.011 to 0.053 in the stations investigated in this research. The highest value of BAF was related to Jozdan station. Comparing the amount of cadmium between different parts of the plant showed that the highest concentration of cadmium with an average of 1.85 mg kg-1 observed in the root. The amount of cadmium in the rice stem also varied from 0.09 (Chamgardan) to 0.32 (Jozdan) mg kg-1 between the studied stations. The values of translocation factor from stem to grain were higher than the values of TF from root to stem, although the values of bioaccumulation factor indicated no accumulation of cadmium in rice grains.

Conclusion

According to the results, rice grains consumption from some of the stations under study may threaten the health of both groups of adults and especially children in the near future. Therefore, in order to maintain food quality and safety, accurate management should be done. Also, it seems necessary to conduct such research in a planned and continuous manner.

Author Contributions

Hamid Reza Rahmani conceived of the presented idea, developed the theory and carried out all stage of the experiment. Zahra Khanmohammadi carried out the statistical analysis, calculated the pollution indices and wrote the manuscript. All authors have read and agreed to the published version of the manuscript

Data Availability Statement

Data is available on request from the authors.

Acknowledgements

The authors would like to thank the Rice Research Institute of Iran and Isfahan Agricultural and Natural Resources Research and Training Center for support of the present study.

Ethical considerations

The study was approved by the Ethics Committee of the Rice Research Institute of Iran (Ethical code: 2-38-04-88039). The authors avoided data fabrication, falsification, plagiarism, and misconduct.

Conflict of interest

The author declares no conflict of interest.

Abbas, T., Rizwan, M., Ali, S., Adrees, M., Zia-Ur-Rehman, M., Qayyum, M. F., Ok Y. S., Murtaza, G. (2018). Effect of biochar on alleviation of cadmium toxicity in wheat (Triticum aestivum L.) grown on Cd-contaminated saline soil. Environmental Science and Pollution Research, 25(26), 25668-25680.
Agricultural statistics, crops of 1401. (1402). Vice President of Statistics Center of Statistics, Information and Communication Technology, Ministry of Agricultural Jihad. (In Persian)
Ahmad, W., Alharthy, R.D., Zubair, M., Ahmed, M., Hameed, A., and Rafique, S. (2021). Toxic and heavy metals contamination assessment in soil and water to evaluate human health risk. Scientific Reports, 11(1): 17006.
Alloway BJ, & Ayres DC. (1998). Chemical principles of environmental pollution (2nd ed.) Blackie Academic and Professional, Chapman and Hall. London.
ATSDR. (2012). Agency for Toxic Substance and Disease Registry, U.S. toxicological profile for cadmium. Department of Health and Humans Services, Public Health Service, Centers for Disease Control, Atlanta, Georgia, USA
Asadi Kapourchal1, S., Homaee, N, and Ramezanpour, H. (2016). Assessing paddy soils contaminated by cadmium in Guilan province using geostatistical methods and GIS. Environmental science, 14(3), 131-146. (In Persian)
Azimzadeh, B., and Khademi, H. (2013). Estimation of Background Concentration of Selected Heavy Metals for Pollution Assessment of Surface Soils of Mazandaran Province. Iran. Journal of Water and Soil, 27(3), 548-559. (In Persian)
Berrow, M.L., Reaves, G.A. (1984). Proceedings International Conference on Environmental Contamination. CEP Consultants; Edimburg, UK: Background levels of trace elements in soils.
BfR Opinion No. 026/2018 (2018) EU maximum levels for cadmium in food for infants and young children sufficient—exposure to lead should fundamentally be reduced to the achievable minimum.
Bhagure, G.R., & Mirgane, S. R. (2011). Heavy metal concentrations in groundwater and soils of Thane Region of Maharashtra, India. Environmental Monitoring and Assessment, 173(1–4), 643–652.
Chapman, H. D., & Pratt, P. F. (1961). Methods of Analysis for Soils, Plants, and Waters. Riverside, CA: University of California.
Cheng, F., Zhao, N., Xu, H., Li, Y., Zhang, W., Zhu, Z., Chen, M. (2006). Cadmium and lead contamination in japonica rice grains and its variation among the different locations in southeast China. Science of the Total Environment, 359(1–3), 156–166.
Cho, U.H., & Seo, N. H. (2005). Oxidative stress in Arabidopsis thaliana exposed to cadmium is due to hydrogen peroxide accumulation. Plant Science, 168, 113-120.
Clemens, S., Aarts, M. G., Thomine, S. & Verbruggen, N. (2013). Plant science: the key to preventing slow cadmium poisoning. Trends in plant science, 18(2), 92-99.
Cui, Y. J., Zhu, Y. G., Zhai R. H., Chen, D. Y., Huang, Y. Z., Oiu, Y., Liang, J. Z. (2004). Transfer of metals from soil to vegetables in an area near a smelter in Nanning, China. Environment International, 30(6), 785–791.
Commission Regulation (EC) No 1881/2006 (2006) Setting maximum levels for certain contaminants in foodstuff.
Department of Environment, (2012). Soil resource quality standards and guidelines. (In Persian)
Gad, S. C. (2014). Cadmium. In Encyclopedia toxicology, edited by Wexler, P. Academic, Oxford, 613–616.
Gilbert, R. O. (1987). Statistical Methods for Environmental Pollution Monitoring. New York: John Wiley & Sons, Inc.
Gill, S.S., Khan, N.A., Tuteja, N. (2012). Cadmium at high dose perturbs growth, photosynthesis and nitrogen metabolism while at low dose it up regulates sulfur assimilation and antioxidant machinery in garden cress (Lepidium sativum L.). Plant Science, 182, 112–120.
Govil, P. K., Reddy, G. L. N., Krishna, A. K. (2002). Contamination of soil due to heavy metals in the Patancheru industrial development area, Andhra Pradesh, India. Environmental Geology, 41(3-4), 461–469.
Hakanson, L. (1980) An ecological risk index for aquatic pollution control: a sedimentological approach. Water Research, 14, 975-1001.
Hang, X., Wang, H., Zhou, J., Ma, C., Du, C., & Chen, X. (2009). Risk assessment of potentially toxic element pollution in soils and rice (Oryza sativa) in a typical area of the Yangtze River Delta. Environmental Pollution, 157(8-9), 2542–2549.
Huang, B., Xin, J., Dai, H., Liu, A., Zhou, W., Yi, Y. & Liao, K. (2015). Root morphological responses of three hot pepper cultivars to Cd exposure and their correlations with Cd accumulation. Environmental Science and Pollution Research, 22, 1151-1159.
Institute of Standards and Industrial Research of Iran (ISIRI), (2021). NO 12968. Food and Feed Maximum limit of heavy metals and test methods. (In Persian)
Isfahan Provincial Agricultural Jihad Organization portal, (1403). (In Persian)
Loska, K., Wiechuła, D., & Korus, I. (2004) Metal contamination of farming soils affected by industry. Environment International, 30, 159-165.
Lindsay, W. L., and Norvell, W. A. 1(978). Development of a DTPA soil test for zinc, iron, manganese and copper. Soil Science Society of America Journal. 42, 421–428.
Liu, W., Zafar, A., Khan, Z.I., Nadeem, M., Ahmad, K., Wajid, K., Bashir, H., Munir, M., Malik, I.S., and Ashfaq, A. (2020). Bioaccumulation of lead in different varieties of wheat plant irrigated with wastewater in remote agricultural regions. Environmental Science and Pollution Research, 27:27937-27951.
Liu, J., Zhang, X. H., Tran, H., Wang, D. Q., Zhu, Y. N. (2011). Heavy metal contamination and risk assessment in water, paddy soil, and rice around an electroplating plant. Environmental Science and Pollution Research, 18(9), 1623–1632.
Mombo, S., Foucault, Y., Deola, F., Gaillard, I., Goix, S., Shahid, M., Schreck, E., Pierart, A. and Dumat, C. (2016). Management of human health risk in the context of kitchen gardens polluted by lead and cadmium near a lead recycling company. Journal of soils and sediments, 16(4), 1214-1224.
Mousavi, S. M., Raiesi, T., Sedaghat, A., & Srivastava, A. (2024). Potentially Toxic Metals: Their Effects on the Soil-Human Health Continuum. Journal of Advances in Environmental Health Research, 12(2), 86-101.
Mousavi, S. M., Srivastava, A. K., & Cheraghi, M. (2023). Soil health and crop response of biochar: an updated analysis. Archives of Agronomy and Soil Siences,69(7),1085-1110.
Muller, G. (1979). Heavy metals in the sediment of the Rhine River. Umsch. in Wisse. Tech, 79:778–783.
Pirzadeh, M., Afyuni, M., & Khoshgoftarmanesh, A. H. (2012). Status of Zinc and Cadmium in Paddy Soils and Rice in Isfahan, Fars and Khuzestan Provinces and their Effect on Food Security. Journal of Water and Soil Science, 16 (60), 81-93. (In Persian)
Rahmani, H. R., & Khanmohammadi, Z. (2020). Effect of Sepahan Cement Factory on Heavy Metals Contamination in Soils of Dizicheh Area of Isfahan. Iranian Journal of Soil and Water Research, 51(7), 1701-1709. (In Persian)
Satpathy, D., Reddy, M.V., Dhal, SP. (2014). Risk assessment of heavy metals contamination in paddy soil, plants, and grains (Oryza sativa L.) at the East Coast of India. BioMed Research International, 2014, 473- 545.
Sebastian, A., & Prasad, M. N. V. (2014). Cadmium minimization in rice. A review. Agronomy for Sustainable Development, 34, 155–173.
Shahid, M., Dumat, C., Khalid, S., Niazi, N. K. and Antunes, P. M. (2016). Cadmium bioavailability, uptake, toxicity and detoxification in soil-plant system. Reviews of Environmental Contamination and Toxicology. 137- 241.
Shi, Z., Garey, M., Meharg, C., Williams, P. (2020). Rice Grain Cadmium Concentrations in the Global Supply‑Chain. Exposure and Health, 12, 869- 876.
Song, W., Chen, S., Liu, J. f., Chen, L., Song, N., Li, N, &. Liu, B. (2015). Variation of Cd concentration in various rice cultivars and derivation of cadmium toxicity thresholds for paddy soil by species-sensitivity distribution, Journal of Integrative Agriculture, 14(9), 1845-1854.
Thévenod, F., and Lee, W.K. (2013). Toxicology of cadmium and its damage to mammalian organs. Metabolism Ions Life Science, 11, 415–490.
Tomlinson, D. L., Wilson, J. G., Harris, C. R., and Jeffrey, D. W. (1980). Problems in the assessment of heavy-metal levels in estuaries and the formation of a pollution index. Helgoländer meeres untersuchungen, 33(1), 566-575.
Tsukahara, T., Ezaki, T., Moriguchi, J., Furuki, K., Shimbo, S., Matsuda-Inoguchi, N., Ikeda, M. (2003). Rice as the most influential source of cadmium intake among general Japanese population. Science of the Total Environment. 305(1–3), 41–51.
USEPA. (2011). Exposure factors handbook 2011 edition (final report). Washington DC: USEPA
Wong, S. C., Li, X. D., Zhang, G., Qi, S. H., Min, Y.S. (2002). Heavy metals in agricultural soils of the Pearl River Delta, South China. Environmental Pollution, 119(1), 33–44.
Wu, S., Xia, X., Lin, C., Chen, X. and Zhou, C. (2010). Levels of arsenic and heavy metals in the rural soils of Beijing and their changes over the last two decades (1985-2008). Journal of Hazardous Materials, 179, 860-868.
Xin, J., and Huang, B. (2014). Subcellular distribution and chemical forms of cadmium in two hot pepper cultivars differing in cadmium accumulation. Journal of Agricultural Food Chemistry, 62, 508-515.
Xu, X., Zhao, Y., Zhao, X., Wang, Y., & Deng, W. (2014). Sources of heavy metal pollution in agricultural soils of a rapidly industrializing area in the Yangtze Delta of China. Ecotoxicology and Environmental Safety, 108, 161–167.
Yu, H. Y., Ding, X., Li, F., Wang, X., Zhang, S., Yi, J. & Wang, Q. (2016). The availabilities of arsenic and cadmium in rice paddy fields from a mining area: the role of soil extractable and plant silicon. Environmental Pollution. 215, 258-265.
Zazouli, M. A., Shokrzadeh, M., Izanloo, H., & Fathi, S. (2008). Cadmium content in rice and its daily intake in Ghaemshahr region of Iran. African Journal of Biotechnology, 7(20), 3686- 3689.
Zhang, M.K., Ke, Z.X. (2004). Heavy metals, phosphorus and some other elements in urban soils of Hangzhou City, China. Pedosphere, 14(2), 177- 185.