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Research Detail

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Mohammad Azizur RAHMAN
Irrigation Management Division, Institute of Water Modelling,Bangladesh,

Jackson ROEHRIG
Institute for Technology in the Tropics, Germany,

The study presented here shows an inadequate dude of groundwater resources in the area comprising Raninagar, Durgapur and Puthia upazilas. Present groundwater withdrawals to attend the water demand for Boro production exceeds actual aquifer recharges and create groundwater resource deficit in these three upazilas. The deficit indicates a non-sustainable situation with increasing draw down. 80% coverage of Boro for all cultivable land of upazilas will incur additional draw downs, for which quite a large number of shallow tubewells need to be replaced by deep tubewell in some places. The river leakage contributes with about 9% of the total recharge for the simulation period 1997-2005. Conjunctive use of surface water and groundwater for irrigation should be promoted and a conjunctive water allocation plan must be established. There is a possibility of increasing groundwater recharge by conservation of surface water in rivers and ‘kharies’ in the post monsoon by retention structures.

  Bangladesh, Recharge assessment, Mathematical modelling, Groundwater, Low Barind
  
  
  
  Resource Development and Management
  Groundwater

The main objective of the proposed study is to apply water resources modelling techniques with the view to increase agricultural production through sustainable utilization of available water resources. The study focuses specially on irrigation adoption based on groundwater availability in order to propose an effective planning and an efficient management of the water resources. The specific objectives for the present study are:
1. Development of mathematical models for the study area using existing hydro-geological and meteorological data including calibration and validation of the model.
2. Assessment of groundwater resources and aquifer recharge, including the assessment of surface water contribution to aquifer.
3. Application of models for various scenarios development.
4. Assessment of groundwater availability as well as potential use for the future.

DESCRIPTION OF THE STUDY AREA The study area is situated in the North-Western part of Bangladesh. The geographic boundary of the study area is 354971E, 691490N for the South-Western corner and 415953E, 755620N for the North-Eastern corner and covers approximately 210800 ha where the cultivated area is about 160952 ha. Bagmara, Puthia, Durgapur, Mohanpur upazilas of Rajshahi district, Raninagar, Manda, Atrai, and Naogaon Sadar upazilas of Naogaon district have been analyzed in the study. The topography of the area varies from 22 meters Public Work Datum (mPWD) in Mohadevpur (in the northern part) to 9 mPWD in Naogaon (in southern part) with a mean of 15.5 m. The study area is relatively flat, sloping towards northeast and southeast, and experiences a tropical humid monsoon climate with flood during monsoon. Annual temperature varies from 10°C to 35°C (MacDonald, 1983). The rainy season is quite wet with a range of 1200 mm to 2100 mm rainfall. Almost 80% of the rainfall occurs during June to October. The relative humidity in the study area varies from 46% to 83% (IWM, 2005). The study area is drained mainly by three major rivers: Atrai, Sib-Barnai, and LNagar, and a number of small rivers, which criss-cross the region. However, there are some low lying areas and small beels in the region. In the study area, the main winter vegetables are Rabi (November to March) crops, while Kharif-I (April to June) crops are HYV Aus, B. Aus, Jute, Kaon, Til and summer vegetables. During the Kharif-II (July to October) grows HYV Aman, local variety Aman and rainy season vegetables. Different fruit trees grow the year round. Irrigation depends mainly on groundwater being extracted predominantly by deep and shallow tubewells (IWM, 2005). Every year new DTW and STW are installed and some tubewells go out of operation. Flooding irrigation is practiced for both DTW and STW. The percentage of currently irrigation coverage is in the range of 72% to 97% of the net cultivable area. DATA ANALYSIS According to the modelling requirements, a significant amount of data has been collected. All the data are secondary and have been obtained from the Institute of Water Modelling (IWM), Bangladesh Agricultural Development Corporation (BADC), Barind Multipurpose Development Authority (BMDA) and Bangladesh Water Development Board (BWDB) etc. In addition to the data quality checking, data analysis also has been carried out for estimation of different model parameters. The subsurface lithological characterization of the study area and the configuration of the hydro-stratigraphic units for groundwater flow model have been prepared. A total of 1233 irrigation well logs from BWDB, BMDA and Local Government Engineering Department (LGED), distributed all over the study area have been reviewed. On the basis of subsurface lithological information, a regional (Manda, Raninagar, Naogaon, Bagmara and Mohanpur) hydrostratigraphic model, fence diagrams and cross-sections have been prepared using RockWorks 2004 software. The hydrostratigraphic model and fence diagram show the presence of two major aquifer systems in the study area, which is separated by a thin aquitard layer. Cross sections prepared for the study area also show that the aquitard 2 and aquitard 3 are not continuous in some places and the both aquifer constitute a big aquifer in those places (see fig. 1). The aquifer layer is composed of medium sand to fine sand, medium sand to coarse sand and occasionally coarse sand. The aquitard layer is composed of clay, silty clay and very fine sand. From the collected aquifer tests data and development tests data the hydraulic conductivity, specific yield and specific storage were calculated and used in the model. From the estimation, it has been found that specific yield varies fron 2% to 25 % and hydraulic conductivity varies from 11.72 m/d to 81m/d throughout the study area. These parameters are adjusted during the model calibration.

  International Conference on Water & Flood Management (ICWFM-2007), 12 - 14 March 2007, BUET, Dhaka, Bangladesh
  
Funding Source:
  

The study area contains two aquifers which are interconnected in many places. Both aquifers are semi-confined, whereas the second aquifer is the main aquifer of the study area. The recharge due to rain and flooding starts in May and continues to the end of October. The groundwater model prepared in this study shows that the average recharge of the groundwater is 398 mm per year (average of year 1997 to year 2005) in the study area, varying from 306 mm (in Puthia Upazila) to 439 mm (in Naogaon Upazila) in the same period. According to the aquifer recharge assessment, irrigation requirements of year 2005 for Boro and extracted water in 2005 depict that Durgapur, Raninagar and Puthia are over exploited areas. According to the model results, the rivers have a positive influence on groundwater recharge. The total recharge for the period 1997 to 2005 (due to rainfall, irrigation and river leakage) is around 800 Mm³/day/year, where as river leakage contributes with around 70 Mm³/day/year, which is about 9% of the total recharge. If the Boro rice production increases to 80% of the net irrigated cultivable area of the upazilas, the groundwater level would drop to about 1m in some places, even more than that in some places. In those places some shallow tubewells might be out of order. According to the prognosis analysis, the groundwater level in dry season will be lowered by 0.2 m per year with the average recharge (year 2001) and current groundwater extraction condition (year 2005). Also in wet season the peak does not recover its original level, probably due to the high extraction if compared to the actual recharge.

  Report/Proceedings
  


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