Md. Billal Hossain*
Ministry of Environment, Forest and Climate Change, Bangladesh Secretariat, Dhaka-1000, Bangladesh
Md. Nurul Islam
Department of Geography and Environment, Jahangirnagar University, Dhaka, Bangladesh
Mohammad Shamsul Alam
Department of Geography and Environment, Jahangirnagar University, Dhaka, Bangladesh
Md. Zakir Hossen
Department of Agricultural Chemistry, Bangladesh Agricultural University, Mymensingh -2202, Bangladesh
Industrialization; Spatial distribution; Wastewater; Sreepur; Gazipur.
Sreepur of Gazipur, Bangladesh
Risk Management in Agriculture
2.1 Description of the Study AreaAccording to physiographic features Sreepur is an area which evolved during Pleistocene period having area of 465.25km².The Upazila is located at the north-eastern part of Gazipur district, which lies between 24°01′ to 24°20′ N latitude and 90°18′ to 90°33′ E longitude. Geologically, the Gazipur cluster lies on the southern corner of Madhupur tract with its average thickness of about 10 m, which consists of over consolidated clayey silt and is underlain by the Pleistocene Dupi Tila formation. The rocks encountered here are much younger in geologic age and ranges between Oligocene and Recent time. The basin has got the record of rapid subsidence and sedimentation. Jamindari system was there like other parts of the then Bengal. “Bhawal Raja" estate was there for long time. By virtue of this, Jamindari system a number of people of this place historically owned handsome amount of land.
2.2 Data Collection about the IndustriesData of the industries in the study area were collected on the basis of the following pre-structured format, viz. serial no., name of the industry, type of industry, category on the basis of ECR, installation of ETP (yes/no), location, GPS point, establishment year and area covered. In case of any query or clarification, industry personnel were asked to reply and sometimes it was discussed also with people living nearby industry. Some of the information was collected on the basis of oral statements and some of the data was collected black and white provided by the industry personnel.
2.3 Water Sampling and processing total of 5 wastewater samples were collected from the study area during three seasons viz. pre-monsoon, monsoon and dry from different points of the canal following the sampling techniques as outlined by APHA [14]. The collected water samples were stored in 500 mL preconditioned clean, high density plastic bottles and use for the analysis of physicochemical parameters. During collection of water samples, bottles were well rinsed using the same water. All the water samples were filtered through Whatman No.1 filter paper to remove unwanted solids and suspended material. After filtration, 3-4 drops of nitric acid were added to the samples to avoid any fungal and other microbial growth. In the laboratory, the samples were kept in a clean, cool and dry place.
2.4 Analytical MethodsThe collected wastewater samples were analysed for various physicochemical parameters, which inclued: pH, electrical conductivity (EC) and total dissolved solids (TDS) were measured within a few hours by using a pH meter (Jenway 3505, UK) and a conductivity meter (SensIONTM+EC5, HACH, USA), respectively. Dissolve oxygen (DO) was determined by Azide modification method, where 2 ml of MnSO4, 2 ml alkali iodide azideand 2 ml of conc. H2SO4 were added as outlined by APHA. Biochemical oxygen demand (BOD) was also determined by Azide modification method, where the samples were kept in a BOD incubator at 20°C for 5 days. The differences between 5 days DO and initial DO was treated as BOD of the water sample. Chemical oxygen demand (COD) was measured by close reflux method using COD vials and measured the concentration by means of a photometer as outlined by APHA.
Asian Journal of Environment & Ecology9(4): 1-14, 2019; Article no.AJEE.50399ISSN: 2456-690X
Journal