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Research Detail

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Md. Kawser Ahmed
Faculty of Earth & Environmental Sciences, University of Dhaka, Dhaka 1000, Bangladesh

Nazma Shaheen
Institute of Nutrition and Food Science (INFS), University of Dhaka, Dhaka 1000, Bangladesh

Md. Saiful Islam
Department of Risk Management and Environmental Sciences, Graduate School of Environment and Information Sciences, Yokohama National University, Yokohama, Kanagawa 240-8501, Japan

Md. Habibullah-Al-Mamun
Department of Fisheries, University of Dhaka, Dhaka 1000, Bangladesh

Saiful Islam
Institute of Nutrition and Food Science (INFS), University of Dhaka, Dhaka 1000, Bangladesh

Md. Monirul Islam
Department of Fisheries, University of Dhaka, Dhaka 1000, Bangladesh

Goutam Kumar Kundu
Department of Fisheries, University of Dhaka, Dhaka 1000, Bangladesh

Lalita Bhattacharjee
National Food Policy Capacity Strengthening Programme, Food and Agriculture Organization of the United Nations, Bangladesh

Arsenic (As), particularly of its inorganic form (iAs) is highly toxic, and its presence in food composites is a matter of concern for the public health safety, specifically in Bangladesh which is regarded as the most arsenic affected country throughout the world. This study was carried out to investigate the levels of As in the composite samples of commonly consumed foodstuffs collected from 30 different agro-ecological zones for the first time in Bangladesh. Most of the individual food composites contain a considerable amount of As which was, as a whole, in the range of 0.077–1.5 mg/kg fw which was lower than those reported from Spain, EU, France, Korea, whereas higher than those of Mexico, Chile, Japan, Cambodia, Hong Kong, Serbia, respectively. Cereals, vegetables, milk, and fish contribute about 90% to the daily intake of inorganic arsenic. Human health risk of dietary iAs was assessed separately for both the rural and urban adults. The estimated daily dietary intakes (EDI) of iAs for the exposed rural (3.5) and urban residents (3.2 μg/kg-BW/day) clearly exceeded the previous provisional tolerable daily intake (PTDI) value of 2.1 μg/kg-BW/day, recommended by the World Health Organization (WHO). From the health point of view, this study concluded that both the rural and urban residents of Bangladesh are exposed to carcinogenic and non-carcinogenic risks who consume As-contaminated water and foodstuffs.

  Arsenic Food chain Health risks
  Faculty of Earth & Environmental Sciences, University of Dhaka, Dhaka 1000, Bangladesh
  
  
  Risk Management in Agriculture
  Arsenic

The identifications of daily dietary intake of arsenic and associated health risk assessment are urgent for both the rural and urban residents in Bangladesh. This study assessed arsenic levels in food composites covering all the agro-ecological zones of Bangladesh and daily dietary intake for both of its rural and urban residents.

2.1. Sample collection and preparation: The per capita per day intake of major food items and intakes of individual food items (BBS, 2011) used to characterize the food consumption pattern of both the rural and urban population in Bangladesh. Both findings showed almost same food composition but different consumption pattern for rural and urban residents. Fresh samples of cereals (Oryza sativa, Triticum aestivum), pulses (Lens culinaris, Cicer arietinum), vegetables (Solanum melongena, Daucus carota, Phaseolus vulgaris, Solanum tuberosum, Solanum lycopersicum, Allium cepa, Capsicum annuum L.), fruits (Musa paradisiaca, Mangifera indica, Artocarpus heterophyllus), freshwater fish (Labeo rohita, Pangasius pangasius, Oreochromis mossambicus), meat (beef, mutton, chicken, duck), egg (chicken, duck), milk (cow) were collected from different rural and urban markets occupying the 30 agro-ecological zones of Bangladesh in 2013. These foodstuffs are highly consumed by the Bangladeshi population as their daily diet (BBS, 2011). A composite of at least 10 samples for each food item was prepared and homogenized in a food processor and 50 g test portions were stored at −20 °C in the Laboratory of the Institute of Nutrition and food Science (INFS), University of Dhaka. The pre-processed samples were then brought to the Laboratory of Environment and Information Sciences, Yokohama National University, Japan and analyzed for arsenic content, expressed as mg/kg fresh weight (wt.). 2.2. Analytical methods 2.2.1. Reagents and sample extraction procedure All solutions were prepared with analytical reagent-grade chemicals and ultrapure water. An arsenic (As) standard stock solution (100 mg L−1 ) for the determination of the total arsenic (tAs) was purchased from Kanto Chemical Co., Inc. (Tokyo, Japan). The internal standard solutions containing 1.0 mg L−1 of indium (In), yttrium (Y), beryllium (Be), telium (Te), cobalt (Co) and titanium (Ti) were purchased from Spex Certi Prep® USA. The connected tube of ICP-MS was inserted into the internal standard bottle and automatically added to the samples during analysis. A solution of 10 mg L−1 multi-element solution (Merck, Darmstadt, Germany) was used to prepare a tuning solution covering a wide range of masses of elements. A microwave digestion system (Berghof, Bavaria, Germany) was used to extract elements from the sample. Digestion reagents that were used included 5 mL HNO3 acid (69%) and 2 mL H2O2 (30%). The weighed samples of 0.3 g were then placed into the digestion reagent in a Teflon vessel. The following microwave program was applied: 10 min at 180 °C with 800 W, 10 min at 190 °C with 900 W, and as a last step 10 min at 100 °C with 400 W. After digestion samples were then transferred into a Teflon beaker and total volume was made up to 25 mL with MilliQ water (Elix UV5 and MilliQ, Millipore, Billerica, MA, USA). The digest solution then filtered (DISMIC® - 25HP PTFE syringe filter (pore size = 0.45 mm); Toyo Roshi Kaisha Ltd., Tokyo, Japan), and stored in a crew cap plastic tube. 2.2.2. Instrumental analysis and quality assurance Arsenic in samples were analyzed using an inductively coupled plasma mass spectrometer (ICP-MS, 7700 series). The detailed analytical procedure of ICP-MS is presented in Table S2. All test batches were evaluated using an internal quality approach and validated if they satisfied the defined internal quality controls (IQCs). For each experiment, a run included blank, an internal standard in samples and samples analyzed in triplicate to eliminate any batch-specific error. A multi-element standard solution was used to prepare a standard curve. Before starting the sequence, RSD (b5%) was checked by using a tuning solution purchased from Agilent Co (Tokyo, Japan). Each analytical procedure was accompanied by a quality assurance program to ensure the quality of the data. The certified reference materials INCT-CF-3-Corn flour from the Institute of Nuclear Chemistry and Technology, Poland, and DORM-2-Dogfish muscle from the National Research Council, Canada, were analyzed to confirm the analytical performance of the applied method. The data of certified reference material (CRM) is presented in Table S3. The limit of detection (LOD) was 0.003 mg/kg with a good precision (2%).

  Science of the Total Environment 544 (2016) 125–133
  
Funding Source:
1.   Budget:  
  

Bangladesh has become dependent upon groundwater as a source of drinking and irrigation water. The ecological systems and population are vulnerable to arsenic contamination due to the ubiquitous nature of arsenic. The groundwater arsenic contamination in Bangladesh and its further spreading into soil and food crops seem to be in a very critical condition. The consumption of arsenic-contaminated food poses a health risk to a larger number of populations in the arsenic affected areas and non-affected areas through their imported food crops from both arsenic-contaminated areas as well and the present critical situation will become severely life-threatening if effective mitigation action plans are not taken as well as implemented immediately. Detailed monitoring programs, mitigation measures, awareness creation, and management of the arsenic problem in Bangladesh are urgently needed from all levels (Government, academicians, NGOs and community) to overcome this burning problem. The overall arsenic contamination scenario needs a comprehensive management plan with respect to conservation and use of surface water bodies, harvesting of rainwater, careful use of uncontaminated groundwater for agriculture, aquaculture, and household purposes. Furthermore, it is important to monitor the food chain because continued use of arsenic-contaminated water and soil is likely to increase the probability and magnitude of dietary arsenic intake which will pose a severe carcinogenic and non-carcinogenic risk to the population.

  Journal
  


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