Sustainable Development of Groundwater
- Dugwell
Based on water-table, depth of weathered material & its
saturation, generalised yield prospects and analysis of hydro-geophysical
properties of aquifer at depth of 11m helped in identifying the area most
suitable ( 195 ha. i.e. 6.60 per cent of study area), suitable ( 310 ha.,
10.16 per cent ) and marginally suitable ( 261.4 ha., 8.82 per cent of study
area ) for groundwater development through dugwell ( Fig. 4 and Table - 1 ) .
Suitable zone is an area where large-scale dugwell development is possible
without disturbing the regional groundwater resources. In the less suitable
area besides groundwater development stress should also be given on
development of surface water harvesting structures. Similarly in marginally
suitable area more stress should be given on development & utilisation of
surface water resource and groundwater development should be given lowest
priority.

Fig. 4 Dugwell development feasibility map of study area
- Dug-cum-borewell
Similarly area suitable for dugwell cum borewell has been
identified which has been further cateogrised into different prospect zone (
Fig. 5 and Table - 1 ) i.e. most suitable ( 118 ha., 3.98 per cent ), suitable
( 338 ha., 11.42 per cent ) and marginally suitable zone ( 672 ha., 22.70 per
cent ). The development as per feasibility map will reduce the chance of over
exploitation of groundwater in area where aquifer is not suitable for dugwell
cum borewell development.
- Deep borewell

Fig. 5 : Dugwell cum borewell development feasibility map of study area
Based on DBTM and hydro-geophysical parameters, total 15.
deep borewell sites have been identified which is supposed to provide
sustainable yield without affecting the regional groundwater environment. Most
of the sites are located in the broader fracture zones or in the sub-surface
basins where high recharge to the aquifer is expected.
Groundwater Development and Management Possibility
In the entire Kewta watershed ( 2961 ha ), 362.42 ha.m
replenished utilisable groundwater reserves are available. The utilisable
groundwater reserve has potential to provide irrigation to 906.00 ha (30.60 per
cent ). Besides that huge amount ( 830 ha. m ) of utilisable groundwater
reserves lies below the existing dugwell depth ( i.e. 10 m b.g.l. ) and basement
surface. This untapped groundwater reserve has potential to irrigated 2075 ha.
(70 per cent ) land ( Table - 2. ). But this untapped groundwater reserves can
only be utilised when suitable recharge mechanism will be developed for
balancing the intake and outtake from the aquifer.
Table - 1: Feasibility for Dugwell and Dug-Cum-Borewell
Development
Dugwell Development Dug-Cum-Borewell Development
Areal extent Per cent Areal extent Per cent
(ha.) ( ha. )
Category
Most suitable zone 195.00 06.60 118.00 03.98
Suitable zone 301.00 10.16 338.00 11.42
Marginally suitable 261.00 08.80 067.00 22.70
Not suitable zone 2204.00 75.42 1833.00 61.90
Table - 2: Groundwater Reserve Estimation
Area of watershed ( ha ), (under consideration) 2961
Aquifer effective porosity / specific yield (per cent) 5.94
Average generalised seasonal fluctuation of water table ( m
b.g.l.) 5 - 10
Replenished groundwater reserve ( ha. m ) 426.38
Utilisable groundwater reserves ( ha. m ) 362.42
Irrigation potential of utilisable groundwater reserves (ha)
906.05
Volume of aquifer material between two extreme of water table
( ha.m ) 8489.14
( i.e. 5 - 10 m b.g.l. )
Volume of aquifer material below 10 m b.g.l up to basement
surface ( ha. m ) 16434.90
Utilisable groundwater reserve lying between 10 m b.g.l. up
to basement
surface ( ha. m ) 830
Irrigation potential of available groundwater reserves below
the 10 m b.g.l ( ha ) 2075
Conclusion
The analysis of hydroheophysical properties of aqufier in
hard rock area has helped in understaing the aquifer properties with limited
geohydrological inputs. On the basis of hydrogeophysical properties, study area
has been cateogarised in different zones for groundwater development and
management. Further DBTM has helped in estimating the groundwater reserve beyond
the replenished reserve by estimating the entire volume of aquifer above the
basement surface. Results indoicate that the groundwater reserve lying below the
lower extrem of watertable ( pre monsoon ) which not replenished at present has
potential to irrigate 2075 ha of land. Therefore there is enough scope for
providing irrigation through groundwater. This can be utilised only when
recharge to the aquifer will increased simultaneouly. The sub-surface basin may
be used for retrieval and storage of groundwater. DBTM has helped in
understanding the lineaments derived from remotely sensed data in better manner.
Acknowledgments
Authors are thankful to Prof. D. P. Singh, Project Director,
Bihar Council on Science and Technology, Patna for giving constant encouragement
for research work. Authors are thankful to Deptt of Science and Technology,
Govt. of India for providing financial assistance to the project.
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