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Research Detail

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M. J. Uddin
Department of Soil, Water and Environment, University of Dhaka, Dhaka-1000, Bangladesh

A. S. M. Mohiuddin
Friends In Village Development Bangladesh (FIVDB), Dhaka-l207, Bangladesh

S. T. Hossain
Friends In Village Development Bangladesh (FIVDB), Dhaka-l207, Bangladesh

Hail haor is located in the Sylhet basin between the Balishira and Satgaon hills under the Moulvibazar district of Bangladesh. In addition, aerial photo of 1984 was used for some verification. The scale used for these two data sources was 1:50,000. ARC/GIS version 7.1 was used in preparing the maps and the subsequent spatial analysis. It is quite evident that a huge amount of sedimentation has taken place in the study sites. This phenomenon of sedimentation over a time periods introduces new soil boundaries along with HYV rice crops which enhance the shrinkage of the water body. In a study MACH (2004) revealed that Hail haor carried over 2,00,000 m3 of sediment just in July, 1999. In 2001, silt loads of 22 hill stream carried 50,000 tons, suggesting that the total of 59 active hill stream carried over 1,00,000 tons of silt into Hail haor each year. Deposition of 8-15 cm of silt in one year was recorded near the outfalls of the hill streams, suggesting that the haor bed is rising on an average by about 5 cm per year (MACH 2004). Hail haor is changing rapidly, the fringes of the haor are rapidly being filled in and it is apprehended that in near future it may disappear.

  Soil, Hail haor, Sylhet basin, Moulvibazar, Eco-environment
  Sylhet Basin of Bangladesh
  
  
  Conservation and Biodiversity
  GIS, Environmental change

Objective of this study was to investigate the eco-environmental changes of the hail haor wetland ecosystem using GIS technology.

Hail haor is located in the Sylhet basin between the Balishira and Satgaon hills under the Moulvibazar district of Bangladesh. The haor originates from the surrounding hill streams. It is a large shallow lake in a saucer-shaped depression, bounded in the south, east and west by low hills and in the north by the plains of the Manu and Kushiara rivers. The haor is almost encircled by a chain of tea estates and natural forest blocks. The river Gopla flows through the wetland in a north-south direction. In order to compare the area of water body, two time series data sources have been taken. The first one is the topographic maps of Messers Capital Air Survey Ltd. Canada during 1974-75 and revised on the ground during 1982-83 and verified during 1987-88 and also 1989-90. The second one is the Land and Soil Resources Utilization Guides of SRDI (2003). In addition, aerial photo of 1984 was used for some verification. The scale used for these two data sources was 1:50,000. ARC/GIS version 7.1 was used in preparing the maps and the subsequent spatial analysis. It is quite evident that a huge amount of sedimentation has taken place in the study sites. This phenomenon of sedimentation over a time periods introduces new soil boundaries along with HYV rice crops which enhance the shrinkage of the water body. The sedimentation process is accelerated with the flow of upstream water from the surrounding hilly areas. As a result, Goainghat-Phagu soil association and Phagu- Hakaluki soil association emerge where HYV boro rice cultivation is gaining popularity with ultimately shrinking the bio-resources of this wetland. The study revealed that the area covered by wetlands in the hail haor has been significantly reduced over the period from 1989 to 2003. According to GIS analysis using PAT (Polygon Attribute Tables) files, total hail haor area was about 10,000 ha in 1989, covering the mapping units of 6, 6a, 7, 7a, 8 and 8a. In 2003, the area of this water body was reduced and the area becomes 5,200 ha covering the mapping unit 6a, 7a and 8a. In 2010, this water ecosystem also decreased significantly and the area of which becomes 2000 ha. The rate of reduction of the water body is alarming but in the dry season, the area of the Hail haor shrinks further which become 900 ha. The study also shows that considerable changes have occurred due to sedimentation and as a result depth and duration of inundation has changed. This change shows a positive impact on agricultural aspects enhancing emergence of new soil boundaries and serious negative impact on eco-environmental aspects i. e. degradation and eduction of wetland ecosystem. Similar findings were also reported by Hoq and Shoaib (2003) and Sultana et at. (2009) in accretion of land for edaphic use in some flood prone areas of Bangladesh (Erickson et al. 1993). Sedimentation has taken place in low lying areas where grazing land emerges in course of time in some flood prone areas. Land use mapping of the surrounding areas of the Hail haor revealed that 46.0 percent is under tea estates, 28.0 percent is forest land and 13.0 percent is privately managed pineapple or other citrus garden (SRDI 2003). These citrus and pineapple gardens disproportionately contributed to siltation because the local farmers habitually grew pineapple and citrus fruits in rows running up-down slope accelerates soil erosion.

  J. Asiat. Soc. Bangladesh, Sci. 39(1): 125-128, June 2013
  
Funding Source:
1.   Budget:  
  

Poor land management in the neighboring hills results in serious soil erosion where pineapple is grown in lines up-down slope. In a study MACH (2004) revealed that Hail haor carried over 2,00,000 m3 of sediment just in July, 1999. In 2001, silt loads of 22 hill stream carried 50,000 tons, suggesting that the total of 59 active hill stream carried over 1,00,000 tons of silt into Hail haor each year. Deposition of 8-15 cm of silt in one year was recorded near the outfalls of the hill streams, suggesting that the haor bed is rising on an average by about 5 cm per year (MACH 2004). Hail haor is changing rapidly, the fringes of the haor are rapidly being filled in and it is apprehended that in near future it may disappear.

  Journal
  


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