Research & Development

Introduction | Historical Background | Major Activities | Development of TARA Pump | Introduction of Mini Tara Pump | Download Research & Development Journal

Introduction:

Ground water is predominant source of water supply system in Bangladesh. In rural areas, water supplies are generally provided by hand pump tube wells which tap water from underground. But in many places, water supplying with hand pump tube wells are facing severe problems due to various reasons. The major reasons are:

  1. Lowering of Water Table.
  2. Water Quality Problem.
  3. Absence of Suitable Water Bearing Formation.
  4. Arsenic Contamination Problem

DPHE is therefore, has been conducing Research and Development activities to improve existing technologies, develop cost effective alternatives and develop alternative technological option to provide water in the problematic areas.

Historical Background:

Considering the problem encountered in rural water supply a technical committee comprising experts from different organizations started their work on Research and Development activities before 1982. Because of water table depletion, hand pump other than #6 was very essential to be introduced in Bangladesh. After a series of discussions, workshop and field verification, TARA hand pump technology for low water table area has been developed in Bangladesh in the year of 1984.

Considering the importance and the magnitude of the R&D activities, it was felt necessary to establish a separate setup of manpower to be engaged in Research & Development activities. Accordingly, DPHE Research and Development Division was created in 1989 under GOB-Unicef project. The R&D committee headed by Superintending Engineer, DPHE Ground Water Circle comprising members from academic institutions, development partner has been playing advisory role on R&D activities since 1992.

In early nineties, detection of arsenic in ground water has caused a threat for ground water based water supply system in Bangladesh. On growing concern over arsenic contamination, a number of studies has been fielded to identify the causes of arsenic contamination, its magnitude and to find out the ways of arsenic mitigating technologies. Apart from this, a number of alternate water options are being explored in the field to evaluate the performance of the options in terms of technical and social aspect.

Major Activities:

Implication of Declining Water Table: Since 1986, DPHE has been monitoring the fluctuations of groundwater table using a measuring network having one tubwell in each union of the country. Measurements are taken once annually during peak dry season. The data indicates the area where the water table has fallen beyond the suction limit has increased from 12% in 1986 to 20% in 1990. As a result a large number of tubewells fitted with no 6 suction pump become non-functioning during dry season. During 1992-95 an in depth study had been carried out to predict the area of the country where the water table would be beyond the suction limit in the year 2010.

Findings on water table monitoring shows that water table has fallen beyond suction limit about 27% in 2004. However, declination of water table should be analyzed for deep and shallow aquifer has been undertaken.

Development of TARA Pump:

Due to declination of water table, a large number of no 6 suction pump started to be inoperative particularly in dry season in different parts of the country. To cope up the problem, Tara pump has been developed based on principle of displacement pump. The pump is submerged in water connected with handle through piston rod. It can yield water within 15meter water table.


Introduction of MINI TARA & Extended piston in 1.5 inch dia shallow well:

It was estimated that a some of 360,000 public tubewells would be inoperative in near future due to gradual declination of water table. To replace these wells by 2-inch dia TARA tubewells was considered to be expensive. In that context, with the support of Unicef, R&D Division had initiated in 1991 to come up modified TARA pump that can fit in the existing diameter of No 6 pump shallow tubewell with minimum modification. The conversions were named as MINI TARA. Initially a test of MINI TARA was performed and 23 nos of such wells were installed. But due to some fault in the design the work was discontinued. However, some development had been made on 10 nos of such wells and tested in the field. 100 Mini Tara were installed in Joydevpur of Gazipur District. Intensive monitoring related to installation technique, performance, maintenance and user’s reaction were done.

In an evaluation over the performance of Mini Tara, it was found that these pump operated well up to 2-3 years. But some difficulties was faced during repairing pump assemble. In that case, back up support is needed to make it sustainable.


Mini Tara Hand Pump

Development of TARA-II and TARA DEV Hand Pump:
TARA hand pumps were installed at 15m depths in low water table areas. In some parts of North Bengal the water table was declining beyond the capacity of Tara pump. To cope up the situation TARA II had been developed and conducted field-test in the year of 1988 to lift water from 30 meters depth. An evaluation by the R&D Committee in early 1992 was indicated that Tara-II fitted with No 6 pump head could be used as an interim solution. Accordingly 150 nos TARA-II tubewells had been installed in later part of 1992-1993 fiscal year. However, further study on these pumps fitted with No 6 head had been carried out to improve the vertical movement of the pump rod. Tara technology having lever action pump is termed as TARA Dev.

Direct action tara and Tara Dev


Concersion of DSP into TARA:
The conventional deep-set pumps were becoming obsolete due to difficulties & expensive maintenance. These wells could easily be converted into TARA, provided the upper well casing remains within water level. 10 nos of such conversion had been made in Ghatail thana of Tangail district. It was proposed to install further 40 such wells to observe the performance; maintenance and construction defect if any to standardize the design.

Water Quality Problem:

Coastal Belt Mapping Updating: In coastal belt areas the major problem encountered in tubewell was salinity of excess concentration. Besides this, in some places no suitable aquifer was available. In 1990-91 a detailed map of the coastal belt was prepared showing different problem areas on it. After that, extensive work to find out suitable water bearing layer was done. By this time some areas were found successful, some areas found unsuccessful for normal hand pump well, where alternate technologies were being applied and some new areas with different problem were identified. All these changes were incorporated in the maps and the coastal belt mapping were updated. The exercise was started in 1993 by conducting 4 workshops in this regard. The activities continued up to 1995 and the maps were again updated.

Danida Supported R & D activities under DPHE- R & D Division
Pond Sand Filters (PSF):

R & D Model PSF:

From the assessment of ITN model PSF it has been revealed that it costly to accommodate by poor household, construction and O & M seems a bit difficult by local private sector and users. Then R & D division has taken initiative to develop a new design. Accordingly the designed has been made and piloted. The design capacity is for about 40 families ie about for 200 users. The estimated cost is about Tk 30000/. The user contribution is 20 % of the estimated cost. It has been monitored for about 7 months for technical, socioeconomic, management and O & M aspects. The findings are satisfactory to be replicated.



Rain water Harvesting System:
R & D division has designed and piloted community based Rain Water Harvesting System (RWHS) to serve 3 to 5 families ie about 25 to 30 users for drinking and cooking purpose. The storage tank volume is 2500litre. The construction cost is about Tk 11000/. The user contribution in construction is 20 % of the estimated cost. The models designed to ensure 7 months water security. It has been monitored for about 7 months for technical, socioeconomic, management and O & M aspects. The findings are satisfactory to be replicated.

Direct action tara and Tara Dev

Piloting on Water Source with Raised Platform:
After 2004 flood, it was planned to construct water source with raised platform in flood shelter or strategic location as emergency preparedness so that the flood distressed people can get water form these sources during flood. In these context water source with raised platform was designed and piloting of 20 no such technologies was carried out in Narsingdi, Lakhmipur, Sylhet and Moulvibazar ( 5 nos at each district).

Narayanpasa Govt. Primary School, Moulovibazar

Jalalabad UP office, Sylhet
In evaluation it was found that water point with raised platform installed in flood shelter ( mostly school or college where people take refuge during flood) or strategic location would be used by the people in normal time and be useful during flood period. Following the findings of piloting, the said technologies were incorporated in the UNICEF assisted Post Flood Rehabilitation project. Under this project about 3500 nos such technologies were installed. After 2007 flood, carried out by CEGIS revealed that these options were very effective during flood.

Pond Sand Filters (PSF):


a. Iron Removal Unit

As a part of the DPHE-UNICEF R & D activities, 10 nos Iron Removal Units have been constructed with different models including using VS ring. Water quality monitoring including its performance evaluation as regard to O&M and acceptability by the community will be start at last part of February 2008. removal of manganese also be include in water quality monitoring programme.

b. Mark-3 and Afridev Technology
It was reported that some part of the country (particularly Rajshahi zone), facing acute lowering of water table exceeding 100 ft. In these areas Tara-dev is not suitable. So Mark-3 and Afridev pump capable of abstracting water having water table around 150 ft. has been taken for piloting under DPHE-UNICEF R&D activities. 5 such tubewells ( 1 in Tongi, 2 in Chapai Nawabganj and 2 in Rajshahi) have already been installed. These technologies will be monitored, reviewed and to be modified for make it more suitable in terms of performance and cost of the technology as well.

c. Safe Water System (SWS): Household Chlorination of Dug well
Piloting on point of use water treatment technologies has been undertaken by DPHE-WHO-UNICEF initiatives. Under these piloting household chlorination is being done in the dugwell of Homna upazilas. EPRC and TWSDA have been engaged as a partner agency. Baseline survey has been completed. Other works like distribution of disinfectant, motivation of the community, testing of water quality is going on.

d. Drilling deep tubewll in gravel problem area

Figure : Three pumps are using as a circuit
In some region in the country including arsenic affected areas, deep drilling is very difficult due to existence of gravel layer. As a part of DPHE-JAICA initiatives, piloting on improvement of water jet method was undertaken to penetrate the gravel layer. Using the said method five deep test drilling have successfully installed in gravel problem areas like Harirumpur of Manikganj and Damurhuda of Chuadanga, Ckowgacha of Jessore, Bera of Pabna. In Bera and Chowgach, arsenic free aquifer could not be found. In Manikganj, more deep drilling will be done using the said method for confirming the deep tubewell as a suitable option in Manikganj areas. The final report is under preparation for printing.

d. Effectiveness of sealing on deep tubewell

According to the protocol of deep tubewell mentioned in Arsenic policy, sealing is to be done to prevent the leaching of arsenic in deep aquifer through drilling hole. Accordingly clay sealing is being done in deep tubewell. But the procedure of clay sealing raised some confusion regarding its effectiveness. In this context as a part of the DPHE-JAICA R&D activities, initiatives has been undertaken to findout the best possible procedure of clay sealing and to examine its effectiveness. Two tubewells of 1.5” diameter were installed at first for experimenting gravel shrouding and clay sealing with clay balls( Clay: Bentonite = 1:1). Three tubewells of 3” diameter were installed and among those one was sealed with cement, one was sealed with clay ball and the rest one without any sealing. Tracer element test was carried out to verify leaking of sealed and without sealing wells. Water samples are now in lab for chemical analysis. Three tubewells of 1.5” diameter were also installed in same methods of which one was sealed with cement, one was with clay ball and the rest one ithout any sealing. Tracer element test for these tubewell will be done very soon. All the tube wells are installed in Kadamtal , Benapole upazila.


 

 
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