تعداد نشریات | 161 |
تعداد شمارهها | 6,532 |
تعداد مقالات | 70,501 |
تعداد مشاهده مقاله | 124,100,419 |
تعداد دریافت فایل اصل مقاله | 97,207,221 |
Hazard Estimations Result from Arsenic Contamination in Common Foodstuffs, Soil, Sediment, and Water of Joypurhat District, Bangladesh | ||
Pollution | ||
دوره 9، شماره 2، تیر 2023، صفحه 531-544 اصل مقاله (757.51 K) | ||
نوع مقاله: Original Research Paper | ||
شناسه دیجیتال (DOI): 10.22059/poll.2022.347351.1578 | ||
نویسندگان | ||
Nazma Khatun* 1؛ Mohammad Nazmul Hossain2؛ Md Didarul Islam3؛ Ashiqur Rahaman4 | ||
1Atomic Energy Centre, Chattogram, Bangladesh Atomic Energy Commission, Chattogram 4209, Bangladesh | ||
2Department of Architecture, Chittagong University of Engineering and Technology (CUET), Chattogram 4349, Bangladesh | ||
3National Institute of Textile Engineering and Research, Dhaka, Bangladesh | ||
4Institute of Leather Engineering and Technology, University of Dhaka, Hazaribagh, Dhaka, Bangladesh | ||
چکیده | ||
We analyzed 125 samples collected from Joypurhat district, Bangladesh, in this study. Average inorganic arsenic (IAs) content obtained from collected polished rice, tomato, potato, radish, and arum leaves 0.31 - 0.91, 0.24 - 0.61, 0.49 - 0.88, 0.40 - 0.93, and 0.30 - 0.69 mg/kg, respectively. This report summarized that almost every agronomic sample contains arsenic; the As contents remain within the permissible limit set by FAO/WHO’s guideline (1.00 mg/kg) except for the rice sample. The As concentration for the rice sample was significantly higher (0.31 - 0.91) than the prescribed limit (0.20 mg/kg). But, the As level for water (mean range, 0.10 - 0.72 mg/l), sediment (0.13 - 0.53 mg/kg), and soil samples (24.1 - 43.1 mg/kg) also significantly surpassed the permissible level. The present study is alarming for water samples, where the highest IAs concentration (0.72 mg/l) is 72 times [14 times] higher than WHO/FAO’s [Bangladesh’s] allowable limit (0.01mg/l) [0.05 mg/l]. All agronomic fields contain higher IAs (25.50 - 43.10 mg/kg) than the world standard limit (10 mg/kg). Statistical Igeo confirmed the moderate pollution of the entire agronomic field of Joypurhat except for the river’s sediment. Again, EF values ensured the anthropogenic pollution by the moderately severe enrichment of As for the 65% agronomic field and significant enrichment of As for the 35% agronomic field. Hazard estimation results revealed the privileged possibility of non-carcinogenic [carcinogenic] health hazards to regular polished rice [water] consumers. So, present study suggests that authorities should take necessary steps to prevent contamination/upcoming health risks. | ||
کلیدواژهها | ||
Heavy metals؛ Pollution؛ Health risk؛ etc | ||
مراجع | ||
Abdullah, M.I.C., Sah, A.S.R.M. and Haris, H. (2020). Geoaccumulation index and enrichment factor of arsenic in surface sediment of Bukit Merah Reservoir, Malaysia. Trop. Life Sci. Res., 31(3); 109-125. Ahmed, M.K., Shaheen, N., Islam, M.S., Habibullah-Al-Mamun, M., Islam, S., Islam, M.M., Kundu, G.K. and Bhattacharjee, L. (2016). A comprehensive assessment of arsenic in commonly consumed foodstuffs to evaluate the potential health risk in Bangladesh. Sci. Total Environ., 544; 125-133. Akter, K.F., Chen, Z., Smith, L., Davey, D. and Naidu, R. (2005). Speciation of arsenic in ground water samples: A comparative study of ce-uv, hg-aas and lc-icp-ms. Talanta., 68(2); 406-415. Alam, M., Snow, E. and Tanaka, A. (2003). Arsenic and heavy metal contamination of vegetables grown in samta village, bangladesh. Sci. Total Env., 308(1-3); 83-96. Ali, M. and Tarafdar, S. (2003). Arsenic in drinking water and in scalp hair by edxrf: A major recent health hazard in bangladesh. J. Radioanal. Nucl. Chem., 256(2); 297-305. ARP (2018). Annual Report Potato, 27-02-18 p. 29. Ministry of Agriculture, Government of the Peoples Republic of Bangladesh. Department of Agricultural Marketing. khamarbari, farmgate, Dhaka-1215.dam.portal.gov.bd/sites/default/files/files/dam.portal.gov.bd/page/dd1bbabf_bcb6_48fe_9c5e_719bcb4d9eff/Annual%20Report%20Potato%2027-02-18.pdf Chakraborti, D., Rahman, M. Mahmudur., Das, B., Murrill, M., Dey, S., Mukherjee, S.C., Dhar, R.K., Biswas, B.K., Chowdhury, U.K., Roy, S., Sorif, S., Selim, M., Rahman, M. and Quamruzzaman, Q. (2010). Status of groundwater arsenic contamination in Bangladesh: A 14-year study report. Water Res., 44(19); 5789-5802. Das, H., Mitra, A.K., Sengupta, P., Hossain, A., Islam, F. and Rabbani, G. (2004). Arsenic concentrations in rice, vegetables, and fish in bangladesh: A preliminary study. Environ. Int., 30(3); 383-87. DoF. Department of Fisheries. (2019). Yearbook of Fisheries Statistics of Bangladesh, 2018-19. Fisheries Resources Survey System (FRSS), Department of Fisheries, Bangladesh: Ministry of Fisheries and Livestock. 36; 2. Dsikowitzky, L., Mengesha, M., Dadebo, E., Eduardo, C., Carvalho, V.D. and Sindern. S, (2013). “Assessment of Heavy Metals in Water Samples and Tissues of Edible Fish Species from Awassa and Koka Rift Valley.” Environ. Monit. Assess., 185; 3117–3131. https://doi.org/10.1007/s10661-012-2777-8. Duxbury, J., Mayer, A., Lauren, J. and Hassan, J. (2003). Food chain aspects of arsenic contamination in bangladesh: Effects on quality and productivity of rice. J. Environ. Sci. Health, Part A., 38(1); 61-69. EPA (2001). Environmental Protection Agency, Parameters of water quality interpretation and standards. 1-133. FAO/WHO, Joint FAO/WHO (2021). Food standards programme, Codex committee on contaminants in foods Food, 14th Session (virtual), 3-7 and 13 May 2021.CF/14 INF/1; (2021); 8-20. Heikens, A. (2006). Arsenic contamination of irrigation water, soil and crops in Bangladesh: Risk implications for sustainable agriculture and food safety in Asia. RAP Publ., (FAO); 1-25. Hossain, M.N., Rahaman, A., Hasan, M.J., Uddin, M.M., Khatun, N. and Shamsuddin, S.M. (2021). Comparative seasonal assessment of pollution and health risk associated with heavy-metals in water, sediment and fish of Buriganga and Turag River in Dhaka city, Bangladesh. SN App. Sci., 3(4); 509-513. IARC, (1993). International Agency for Research on Cancer, Beryllium, cadmium, mercury and exposure in glass manufacturing industry. Vl.58. IARC, Lygon, France. (1993) p. 119238 Islam, M.D., Hasan M.M., Rahaman A., Haque P., Islam M.S. and Rahman M.M. (2020). “Translocation and Bioaccumulation of Trace Metals from Industrial Effluent to Locally Grown Vegetables and Assessment of Human Health Risk in Bangladesh.” SN App. Sci., 2 (8); 1–11. https://doi.org/10.1007/s42452-020-3123-3. Khatun, N., Nayeem, J., Deb, N., Hossain, S. and Kibria, M.M., (2021). Heavy metals contamination: possible health risk assessment in highly consumed fish species and water of Karnafuli River Estuary, Bangladesh. Toxicol. Environ. Health Sci., 13 (12); 122-136 Kundu, A.K., Majumder, S., Biswas, A., Bhowmick, S., Pal, C., Mukherjee, A., Majumder, M. and Chatterjee, D. (2018). Optimisation of laboratory arsenic analysis for groundwaters of west bengal, india and possible water testing strategy. Int. J. environ. anal. chem., 98(5); 440-452. Langasco, I., Barracu, F., Deroma, M.A., López-Sánchez, J.F., Mara, A., Meloni, P., Pilo, M.I., Estrugo, À.S., Sanna, G., Spano, N. and Spanu, A. (2022). Assessment and validation of ICP-MS and IC-ICP-MS methods for the determination of total, extracted and speciated arsenic. Application to samples from a soil-rice system at varying the irrigation method. J. environ. manag., 302; 114105. Lyu, B., Li, J. and Wu, Y., (2022). Characterizing the exposome of food contamination and China Total Diet Study: project for improving food safety risk assessment in China. Chin. CDC Week., 4(9); 157. Ma, L., Wang, L., Tang, J. and Yang, Z. (2016). Optimization of arsenic extraction in rice samples by plackett–burman design and response surface methodology. Food chem., 204; 283-88. Meharg, A.A. and Rahman, M.M. (2003). Arsenic contamination of bangladesh paddy field soils: Implications for rice contribution to arsenic consumption. Environ. Sci. Tech., 37(2); 229-34. Mehrdadi, N., Nabi, R. and Nasrabadi, T. (2009). “Monitoring the Arsenic Concentration in Groundwater Resources, Case Study: Ghezel Ozan Water Basin, Kurdistan, Iran.” Asian J. Chem., 21 (1); 446–50. Mihucz, V.G., Enesei, D., Veszely, A., Bencs, L., Pap-Balazs. T., Ovari, M., Streli, S. and Zaray, G. (2017). A simple method for monitoring of removal of arsenic species from drinking water applying on-site separation with solid phase extraction and detection by atomic absorption and x-ray fluorescence based techniques. Microchem. J., 135; 105-113. Nasrabadi, T., Maedeh, P.A., Sirdari, Z.Z., Bidabadi, N.S., Solgi, S. and Tajik, M. (2015). “Analyzing the Quantitative Risk and Hazard of Different Waterborne Arsenic Exposures: Case Study of Haraz River, Iran.” Environ. Earth. Sci., 74 (1); 521–32. https://doi.org/10.1007/s12665-015-4058-7. Nasrabadi, T., and Bidabadi, N.S. (2013). “Evaluating the Spatial Distribution of Quantitative Risk and Hazard Level of Arsenic Exposure in Groundwater, Case Study of Qorveh County, Kurdistan Iran.” Iran. J. Environ. Health Sci. & Eng., 10 (1); 1–8. https://doi.org/10.1186/1735-2746-10-30. Phan, K., Sthiannopkao, S., Kim, K.W., Hung, M., Sao, V., Hisham, J., Salleh, M. and Yasin, M.2010. “Health Risk Assessment of Inorganic Arsenic Intake of Cambodia Residents through Groundwater Drinking Pathway.” Water Res., 44 (19); 5777–88. https://doi.org/10.1016/j.watres.2010.06.021. Rahaman, M.S., Mise, N. and Ichihara, S. (2022). Arsenic contamination in food chain in Bangladesh: A review on health hazards, socioeconomic impacts and implications. Hygiene Environ. Health Adv., 2; 100004. Rahman, H.H., Niemann, D. and Munson-McGee, S.H. (2022). Association of albumin to creatinine ratio with urinary arsenic and metal exposure: evidence from NHANES 2015–2016. Int. Urol. Nephrol., 54(6); 1343-1353. Raju, N.J. (2022). Arsenic in the geo-environment: A review of sources, geochemical processes, toxicity and removal technologies. Environ. res., 203; 111782. Reimers, K.J. and Keast, D.R. (2016). Tomato consumption in the United States and its relationship to the US Department of Agriculture food pattern: results from What We Eat in America 2005–2010. Nutr. Today., 51(4); 198-205. Roychowdhury, T., Uchino, T., Tokunaga, H. and Ando, M. (2002). Survey of arsenic in food composites from an arsenic-affected area of west bengal. India. Food Chem. Toxicol., 40(11); 1611-21. Sadee, B.A., Foulkes, M.E. and Hill, S.J. (2016). A study of arsenic speciation in soil, irrigation water and plant tissue: A case study of the broad bean plant, Vicia faba. Food chem., 210; 362-370. Sapunar-Postružnik, J., Bažulić, D. and Kubala, H. (1996). Estimation of dietary intake of arsenic in the general population of the republic of Croatia. Sci. total environ., 191(1-2); 119-23. Schoof, R., Yost, J. and Eickhoff, E. (1999). Crecelius D, Cragin D, Meacher and Menzel D. A market basket survey of inorganic arsenic in food. Food Chem. Toxicol., 37(8); 839-46. Suzuki, Y., Kondo, M., Harimoto, M., Kitayama, I. and Akiyama, H. (2022). Dietary exposure to arsenic species in Japan in 2019 using a total diet study based on composite sample with market basket approach at the national level. J. Food Compos. Anal.,108; 104384. Taylor, S.R. (1964). Abundances of chemical elements in the continental crust: a new table. Geochim. Cosmochim. Acta., 28; 1273-1285. doi: 10.1016/0016-7037(64)90129-2 Tsuda, T., Inoue, T., Kojima, M. and Aoki, S. (1995). Market basket and duplicate portion estimation of dietary intakes of cadmium, mercury, arsenic, copper, manganese, and zinc by japanese adults. J. AOAC Int., 78(6); 1363-68. USEPA. , (2015). United State Environmental Protection Egency, (2015). Human health risk assessment, Regional screening levels (RSL), Summary table. http://www.epa.gov/reg3hwmd/risk/human/rb_concentrationtable/Generic_Table/does/master_sl_table_run_JAN 2015.pdf. WHO, (2017). World Health Organization’s Guidelines for drinking water quality. Wong, C., Roberts, S.M. and Saab, I.N. (2022). Review of regulatory reference values and background levels for heavy metals in the human diet. Regul. Toxicol. Pharm., 130; 105122.6 | ||
آمار تعداد مشاهده مقاله: 471 تعداد دریافت فایل اصل مقاله: 651 |