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Research Detail

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Ram Proshad
Department of Soil Science, Patuakhali Science and Technology University, Patuakhali, Bangladesh;

Tapos Kormoker
Department of Emergency Management, Patuakhali Science and Technology University, Patuakhali, Bangladesh;

Md. Saiful Islam
Department of Soil Science, Patuakhali Science and Technology University, Patuakhali, Bangladesh; Department of Applied Biological Chemistry, Graduate School of Agricultural and Life Sciences, The university of Tokyo, Tokyo, Japan

Krishno Chandra
Department of Chemistry, Goverment Saadat College, Tangail, Banglades

Heavy metals are toxic in nature, and their contamination in food-stuff is a matter of concern for human health. The present study was conducted to assess the concentrations of chromium, nickel, copper,arsenic, cadmium, and lead in rice and vegetables and their possible human health risks in Tangail district, Bangladesh. Metals were measured by inductively coupled plasma mass spectrometry (ICP-MS) after microwave digestion system. The average values of Cr, Ni, Cu, As,Cd, and Pb in rice and vegetables were 16.26, 16.11, 13.99, 2.28,1.86, and 7.93 mg/kg, respectively. The average metal concentration in rice and vegetable species was in the decreasing order of okra>-chili>bitter gourd>papaya>brinjal>bean>bottle gourd>rice>cucumber>sponge gourd>Indian spinach. The estimated daily intake (EDI) values of all the metals except Cu were higher than the maximum tolerable daily intake (MTDI). The target hazard quotients (THQs) values of Ni, Cu, As, Cd, and Pb exceeded the threshold value of 1 through consumption of rice and vegetables, indicating significant health risks to both adult and children. The target carcinogenic risk (TR) of As and Pb through consumption of rice and vegetables was higher than the USEPA threshold level (104). From the health point of view, this study clearly revealed that consumption of these contaminated rice and vegetables definitely poses carcinogenic and non-carcinogenic risks

  Heavy metals; Rice; Vegetables; Health risk; Bangladesh
  Tarutia, Tangail Sadar Upzila of Tangail district, Bangladesh
  
  
  Risk Management in Agriculture
  Heavy metal, Vegetables, Rice

The objectives of this study were to evaluate the concentration of six heavy metals in agricultural crops that are usually consumed by the Bangladeshi population and to assess the potential health risk in terms of dietary intake, target hazard quotient (THQ) and target cancer risk for the local inhabitants of Tangail district, Bangladesh

Study area The samples were collected from Tarutia, Tangail Sadar Upzila of Tangail district, Bangladesh. Tangail district area is 334.26 km2and situated at the middle part in Bangladesh. Tangail Sadar Upazila is densely populated area in Bangladesh and population density is 1,100 /km2 (BBS2011). The study area is situated between Tangail Sadar is located at 24.2500N to 89.9167E. Tangail as an industrial vicinity of Bangladesh possesses highly vulnerable to environmental pollution. There are different kinds of industries in Tangail district such as garments, packaging industry, dyeing,brick kiln, metal workshops, battery manufacturing industries, tanneries, textile industries, pesticide and fertilizer industries, different food processing industries which pro-duce huge volumes of effluents that contain heavy metals. After production, these industries discharge untreated wastes randomly to river and canals (Proshadet al. 2017). Then, the disposed wastes are mixed with soils and the soil is continuously being polluted by toxic elements in Bangladesh. Rice and vegetable sampling Rice and vegetables were collected near industrial vicinity, and at each sampling station,same species of rice and vegetables were collected as sub-samples and were thoroughly mixed to form a composite sample. One hundred and thirty-five samples of eleven different agricultural crops i.e. rice (Oryza sativa), sponge guard (Luffa cylindrical), bittergourd (Momordica charantia), papaya (Carica papaya), okra (Abelmuschus esculentus), bean (Phaseolus vulgaris), brinjal (Solanum melongena), chili (Capcicum frutescens), Bottle gourd (Lagenaria siceraria), Cucumber (Cucumis sativus), and Indian spinach (Basella alba) were collected by hand from the selected agricultural fields during March–April 2017. Plant samples were collected for chemical analysis kept in polythenezip bags with definite marking and tagging and brought to the laboratory on the day of sampling. Rice and vegetable samples were washed with distilled water and cut into small pieces and was kept in oven at 70–80C to attain constant weight (Tiwariet al. 2011). The fresh and dry weights were recorded to calculate moisture contents. The processed samples were brought to Yokohama National University, Japan, for chemical analysis. Heavy metal analysis All chemicals were analytical grade reagents; Milli-Q water (Elix UV5 and Milli-Q, Millipore, Boston, MA, USA) was used for the preparation of solutions. The Teflon vessel and polypropylene containers were cleaned, soaked in 5% HNO3 for more than 24 h,then rinsed with Milli-Q water and dried. For metal analysis, 0.3–0.5 g of the food sample was treated with 6 mL 69% HNO3 (Kanto Chemical Co, Tokyo, Japan) and 2 mL 30% H2O2 (Wako Chemical Co, Tokyo, Japan) in a closed Teflon vessel and was digested in a Microwave Digestion System (Bergh of speedwave1, Eningen, Germany). The digested samples were then transferred into a Teflon beaker, and a total volume was made up to 50 mL with Milli-Q water. The digested solution was then filtered by using syringe filter (DISMIC1–25HP PTFE, pore size¼0.45 mm; Toyo Roshi Kaisha, Ltd., Tokyo, Japan) and stored in 50-mL polypropylene tubes (Nalgene, New York, NY,USA). After that, the digestion tubes were then cleaned using blank digestion procedure following same procedure of samples. For heavy metals, samples were analyzed using inductively coupled plasma mass spectrometer (ICP-MS, Agilent 7700 series, Santa Clara, CA, USA). Instrument operating conditions and parameters for metal analysis are done. The detection limits of ICP-MS for the studied metals were 0.7, 0.6, 0.8, 0.4,0.06, and 0.09 ng/L for Cr, Ni, Cu, As, Cd, and Pb, respectively. Multi-element StandardXSTC-13 (Spex CertiPrepVR, Metuchen, NJ, USA) solutions were used to prepare calibration curves. Internal calibration standard solutions containing 1.0 mg/L of indium (In),yttrium (Y), beryllium (Be), tellurium (Te), cobalt (Co), and thallium (TI) were purchased from Spex Certi PrepVR (Metuchen, NJ, USA). During the procedure, 10 mg/Linternal standard solution was prepared from the primary standard and added to the igested samples. Multi-element solution (purchased from Agilent Technologies, Japan) was used as tuning solution covering a wide range of masses of elements. All test batches were evaluated using an internal quality approach and validated if they satisfied the defined Internal Quality Controls (IQCs). Before starting the analysis sequence, relative standard deviation (RSD,<5%) was checked by using tuning solution purchased from Agilent Technologies. The certified reference materials INCT-CF-3 (corn flour) bought from the National Research Council (Canada) were analyzed to confirm analytical performance and good precision (relative standard deviation bellow 20%) of the applied method.

  HUMAN AND ECOLOGICAL RISK ASSESSMENT 2020, VOL. 26, NO. 4, 921–943
  https://doi.org/10.1080/10807039.2018.1546114
Funding Source:
1.   Budget:  
  

The present study revealed that the concentrations of Cr, Ni, As, Cd, and Pb in rice and vegetables were higher than the WHO and FAO permissible limit. The concentration of metals in studied food samples was in the decreasing order of Cr>Ni>Cu>Pb>As>Cd. Multivariate analysis showed that Cr, Ni, As, Cd, and Pb in food samples were mostly contributed by industrial activities. The total EDIs of Cr, Ni, Cd, and Pb from all studied food samples were higher than the MTDI assumed that these metals had the major contribution to the potential health risk via food consumption in the study area. The THQ values of Ni, Cu, As, Cd, and Pb exceeded the thresh-old value (>1), and the consumers are at high risk with respect to Ni, Cu, As, Cd, and Pb which can cause non-carcinogenic risks. Hazard index for adult and children resulting from exposure to metals through rice and vegetables intake indicated that the investigated species were not safe for human consumption. The total carcinogenic risk of As from the foodstuffs was higher than 104indicating cancer risk to the both adult and children in the study area and the risk for Pb from most of the foods was in the line of acceptable level of 104. Continuous consumption of these food items definitely poses cancer risks to the study area people.

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