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Research Detail

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M. Aktaruzzaman
Department of Environmental Sciences, Jangirnagar University, Dhaka - 1342, Bangladesh

A.N.M. Fakhruddin
Department of Environmental Sciences, Jangirnagar University, Dhaka - 1342, Bangladesh

M.A.Z. Chowdhury
Agrochemial & Environmental research Division, IFRB, AERE Savar, Dhaka - 1349, Bangladesh

Z. Fardous
Agrochemial & Environmental research Division, IFRB, AERE Savar, Dhaka - 1349, Bangladesh

M.K. Alam
Agrochemial & Environmental research Division, IFRB, AERE Savar, Dhaka - 1349, Bangladesh

Accumulation of heavy metals in environmental matrices is a potential risk to living system due to their uptake by plants and subsequent introduction into the food chain. A study was conducted to investigate the heavy metals concentration in soils and leafy vegetables samples along the Dhaka Aricha Road to assess their potential ecological risk. Heavy metals concentration was analyzed by Atomic Absorption Spectroscopy. Concentrations of all the tested heavy metals except Cd in soil samples were below the permissible level. The mean concentration of Cd was found 3.99±1.85 mg kg-1. Concentrations of all the tested heavy metals except Cd and Cr in vegetables samples were lower than recommended level. Mean concentration of Cd and Cr were found 1.00 ± 0.68 mg kg-1 and 2.32±0.84 mg kg-1, respectively. Based on the Potential Ecological Risk Index, Cd posed very high risk to the local ecosystem due to its higher Risk Factor, >320 and based on Transfer Factor of Pb and Cd were found higher accumulator among the tested metals. The results of present study revealed that the bioconcentration of heavy metals along the Dhaka Aricha Road posed high risk to the ecosystem. Considering the Transfer Factor of Cd and Pb it can be suggested that plants and leafy vegetables grow in the soil near Dhaka Aricha Road should not be used as food or feed.

  Heavy metals, Leafy vegetables, AAS, Transfer factoe, Ecological risk factor
  Department of Environmental Sciences, Jangirnagar University, Dhaka
  
  
  Risk Management in Agriculture
  Heavy metal

The aim of the present study was to determine the concentrations of heavy metals in soil vegetables samples along the Dhaka Aricha road, Savar, to assess the potential ecological risk posed by heavy metals and Transfer Factor of heavy metals in the soil-vegetables system.

Reference standard for heavy metals: Reference standard heavy metals Cadmium, Copper, lead, Chromium, Manganese, Iron and Zinc were obtained from Kanto Chemical Co. Inc. Hydrochloric acid and Nitric acid were obtained from Merck.

Description of the study area: The area selected for the study was along the Dhaka Aricha Road and near the Savar area about 17 km north from Dhaka centre and runs northward. The site was selected for this study because it links capital Dhaka city Dhaka and it has a comparatively high traffic density. The study site is also exposed to different degrees of industrial pollution especially textile dying industries.

Collection of soil sample: Soil samples (1 kg each) were collected from along the Dhaka Aricha Road. Polyethylene bags were used for collecting the soil sample. The samples were transferred to the laboratory as early as possible. The samples were properly labeled and preserve at -20°C to preclude the risk of hydrolysis and oxidation.

Collection of vegetables sample: Fresh leafy vegetables (Red Spinach) samples were randomly collected from the sides along the Dhaka Aricha road. Vegetables samples were stored in polyethylene bags in the field, the samples were transferred to the laboratory as early as possible. Samples were directly oven dried at temperature of 75°C for 24 h and then finally crushed and sieved at room temperature conditions. The sieved samples were stored in airtight sealed plastic bottles until required for analysis.

Soil sample preparation and digestion procedure: Soil samples were oven dried at 95°C for 48 h and ground into fine powder using pestle and mortar. Further 15 g of fine powder sediment sample was taken in a conical flask to which 15 mL of 1M HNO3 were added. Then 30 mL of distilled water was added to the mixture and the solution kept 24 h. After 24 h distilled water was added to the solution and making the solution 150 g by weight and the sample was centrifuged and filtered by Whatman No. 41 filter paper. Filtrates were then analyzed by AAS.

Vegetable sample preparation and digestion procedure: Samples were digested with Nitric acid for heavy metal determination. Once collected, samples were first washed with normal tap water. All washed samples were carefully air dried, cut into small pieces and drying in the oven at 60°C for 24 h until samples became fully dry. This was followed by grinding and homogenization of the dried samples into fine powder using an electric grinder. The powdered samples are then stored in closed containers in absence of humidity. Vegetables samples (1.00±0.001 g) were placed into crucible, to which 10 mL of acid 65% high purity HNO3 was added. The mixture was then digested at 60°C till the solution became semi dried. Again 10 mL of con HNO3 and 4 mL of H2O2 was added and again kept on hot plate for 1 h. After getting semi dried than cooled and filtered with the help of what men filter paper. Volume of the residues was made up to 50 mL with 2 M HNO3· Finally, the solution was analyzed.

Determination of heavy metal concentrations of soil and vegetables samples: Atomic Absorption Spectroscopy (AAS) (Model: AA-6401F, Shimadzu, Made in Australia), was used for the determination of heavy metals. To provide element specific wavelengths, a light beam from a lamp whose cathode is made of the element being determined is passed through the flame.

  Pakistan Journal of Biological Sciences, 16: 332-338; ISSN 1028-8880
  DOI: 10.3923/pjbs.2013.332.338; URL: http://scialert.net/abstract/?doi=pjbs.2013.332.338
Funding Source:
1.   Budget:  
  

Concentrations of all the heavy metals except Cd (mg kg-1 Dw) in the studied soil were below the permissible level. The mean concentration of Cd was found 3.99±1.85 mg kg-1. Concentrations of all the heavy metals except Cd and Cr in vegetables samples were lower than recommended levels. Mean concentrations of the Cr and Cd were found 2.32±0.84 and 1.00±0.68 mg kg-1, respectively.  Cd poses very high risk to the local ecosystem according to Grades of ecological risk of metals (Eri) value, which was >Eri 320. The overall risks levels of heavy metals were in order of Cd>Pb>Cu>Cr>Zn. According to the soil to plant Transfer Factor (TF) calculated for tested metals and leafy vegetables consumed by local residents, it can be concluded that Pb and Cd was high accumulator among the investigated metals. The trend of TF for heavy metal in vegetable samples studied was in order of: Pb>Cd>Zn>Cu>Cr.

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