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ABOUT US South Western Region, Bangalore has its jurisdiction of Karnataka and Goa States. These States are looked after by the Regional office, Drilling division and Unit office located at Bangalore and Belgaum respectively.
Central
Ground Water Board, SouthWestern Region has its jurisdiction of
Karnataka and Goa States. Theses States are looked after by the
Regional office and Unit office located at Bangalore and Belgaum
respectively. The region came into existence in June 1982.The unit office
which was established in 1969 and existing in Bangalore was shifted to
Belgaum in 1986. Karnataka State having an areal extent of 1,91,791
sq.km. is divided into
26 districts and 175 taluks. The State is comprising of four distinct
physiographic units viz., (i) Northern table land (ii) Southern table land
(iii) Malnad region with hills and valleys
(iv) Narrow coastal plain along the west coast Cauvery,
Thungabhadra, Krishna, Godavari, Palar, Pennar and west flowing
rivers like Netravathi, Kali are the major river systems drain
in the State. The rainfall pattern varies from 30
to 600 cm per annum. Crystallines
and Metamorphic rocks cover 97% of the area and 3%
is covered by alluvium along the coast and major rivers. Goa
State covers an area of 3702 sq.km, comprises of two
districts namely North Goa and South Goa. The distinct physiographic units
of Goa comprises of Western ghat hills in the west graded down to well
dissected plateau in the middle and coastal plain in the east. Among nine
rivers draining in the State, rivers like Terekal, Chapara, Zuari, Mondovi
are the important ones. Metamorphic rocks like phyllites, schists.
granites and gneisses are the important rock types apart from
alluvium which is restricted along the coast. Laterite occurs
extensively in the state where the occurrence of groundwater
encountered commonly.
The work programme
is broadly covered under following activities. *
Systematic and reappraisal hydro geological surveys. *
Exploratory drilling. *
Ground water regime monitoring. *
Hydro chemical analysis. Remote sensing, Geophysical, Hydrological,
and
Hydro meteorological studies. *
Ground water resource estimation. *
Special project studies like artificial recharge and conjunctive
use projects *
Assistance to State government and semi government
organisations,Public
sector undertakings including Technology Mission for Rural water
supply. *
Pollution Studies like Ground Water In land salinity, Coastal Salinity and
Land fill
studies in urban areas etc. *
Hydrology project. *
Preparation and issuance of various reports and maps. STATUS OF WORK
: Activities
undertaken during various Annual Action Plans of Central Ground Water
Board, SouthWestern Region, Bangalore, is presented below.
1.
SYSTEMATIC AND REAPPARAISAL HYDRDOGEOLOGICAL SURVEYS 2.
EXPLORATORY DRILLING Under
the first approximation resource evaluation studies as stated above
various types of bore holes like exploratory, observation and piezometer
wells have been drilled for generating scientific data in various
geological formations of Karnataka. This information includes the thickness of weathered layer,
occurrence of fractures in crystallines and vesicular zones in deccan
basalts, cavernous limestones, and potential zones in coastal alluvium.
The slim hole drilling have been attempted in the coastal area of Dakshina
Kannada district and in other geological formation of Karnataka to
understand the subsurface geology and to adopt a suitable methodology for
the construction of production wells. To study the behavior of ground
water levels in time and space, piezometer and piezometer nests were
constructed to study the phreatic and other aquifers. A brief of various
salient data of drilling programme in Karnataka and Goa are presented
below. MULTI
DISIPILINARY STUDIES (a)
Karnataka (b)
Goa Table:
1 Yield range of exploratory bore wells tapping different aquifers in
Karnataka.
Table
2 : Talukwise distribution of exploratory and observation wells in Goa
State.
Total for Goa State 54+19 = 73 nos. The
major aquifers are in granites and granite gneisses, meta-basalts,
meta-sediments metagrey wackes and alluvium.
The formation wise distribution of exploratory and observation
wells are tabulated in table.3
Based on litho logs of select 19 exploratory wells in the
state, it is inferred that in the northern, Northwestern part and in
central Goa laterite thickness is predominant, whereas on the eastern
fringe areas and southern parts of Goa State the same is negligible or
nil. Further in Salcete taluk,
alluvium of 12-21m thickness rest on granites and gneisses. Table.3 Formation/Aquifer wise distribution of exploratory and
observation wells in Goa State.
Aquifer
parameters of fractured rocks (deeper zones) Down
to the basement ground water occurs in planar porosities such as joints,
fractures and its movement is controlled by geometry of structural weak
planes and their inter- connection rather than morphological control as in
the case of water table aquifers. The
water in them exists either in confined or semi-confined state. Unlike
granular unconsolidated sediments, these fractured rocks exhibit lateral
and vertical anisotropism in yield and aquifer parameters, which is
tabulated in table.4 Alluvial
aquifers, metabasalts, metagreywacks and meta sediments (mostly schists,
fractured quartzites and phyllites) are better aquifer than granites and
gneisses. Exploratory wells
in meta-basalts, metagreywackes and metasediments falling on well defined
intersecting weak planes have yields from 9.9 to 13 lps with a draw down
in a range from 1.18 to 18m. Some
of the exploratory wells falling on open intersecting fractures are given
in table.5 Handing
over of exploratory wells The
status of Handing over of exploratory wells in Karnataka is as follows: As per the recent
decision conveyed by the Ministry, The wells were offered by Central
Ground Water Board on free of cost for the effective utilization of the
State Govt. to put into use of these wells for water supply schemes. High
yielding wells constructed by CGWB in drought districts of Karnataka will
be immense of use during drought mitigation time. As per the status
position of handing over of exploratory wells is concerned exploratory
wells drilled in Karnataka and Goa
State have been handed the States accordingly. Table: 4
Range of yield characteristics and aquifer parameters
for important fractured aquifers
in Goa State.
A
= Range in Parameters, B =
Average of Parameters. Table:5
Hydrological parameter of various aquifers tapped in Goa State
3.
NATIONAL HYDROGRAPH NETWORK STATION MONITORING PROGRAMME
Monitoring of ground water levels through a network of observation
wells is essential to assess the effects of rainfall and the impact of
withdrawal ground water for the developmental work on the ground water
regime. In a Hydrogeological system the impact of recharge due to
infiltration and discharge due to extraction is reflected through rise or
fall of ground water levels. Rainfall being the major component of
recharge to ground water, infiltration of part of the rain water during
the monsoon period produces a recharge to ground water resulting in a rise
in ground water levels. During post monsoon period extraction of ground
water is the dominant feature and this results in a decline in ground
water levels till the onset of monsoons.
In Karnataka Central Ground Water Board had a network of 1206
observation wells as on March 2000. Subsequently some of the network
stations that were filled up/closed/consistently dry were abandoned, thus
reducing the total network to 1132 stations (table.6). The network
observation stations are monitored four times a year during the months of
May (pre monsoon), August (mid monsoon), November (post monsoon) and
January (non monsoon). The water levels thus collected have been
critically analysed to determine the following features namely, a.
Distribution of ground water levels. b.
Seasonal and annual fluctuation in ground water levels and decadal change
in storage. The
observations on ground water level behavior in Karnataka and Goa are
described below. 3.1
Karnataka:
During the pre monsoon (May) period the depth to water levels are
deeper than the other measurements as withdrawal from ground water is the
dominant component prior to these measurements. The pre-monsoon water
levels recorded in Karnataka ranged from 0.17 to 24.43 mbgl. Shallow water
level of 2 to 5m has been recorded in parts of Bidar, Gulbarga, Raichur,
Bellary, Bagalkot, Gadag, Koppal, Davanagere, Chikamagalur, Shimoga,
Mandya, Mysore and Bangalore districts.
The shallow water levels are due to canal irrigation in some parts
and less stress in terms of ground water development in others. The water
level of 5 to 10 m is the general water level occurring throughout the
state in parts of almost all the districts and recorded in 47% of the NHNS. Moderately deep water level of 10 to 20 mbgl occurs in about 24% of
NHNS as pockets scattered throughout the state with larger areal extent in
parts of Bidar, Dharwar, Gadag, Haveri, Koppal, Shimoga and Davanagere
districts. These deeper water level parts represent the areas of higher
ground water stress in terms of draft. Water level of >20 mbgl has been
recorded as localized pockets in parts of Bidar, Bagalkot, Belgaum, Haveri
and Mandya districts which account for about 1% of the data analysed.
During the post monsoon (November) period the depth to water level
ranged from 0.13 to 22.86 mbgl. It is observed that about 90% of the state
area have water levels within 10 mbgl. 2 to 5 mbgl and 5 to 10 mbgl are
the general water levels occurring throughout the state found in parts of
almost all the districts of the state.
Shallow water level of less than two metre is recorded in parts of
Bidar, Gulbarga, Belgaum, Dharwar, Raichur, Koppal, Shimoga, Mysore,
Mandya and Bangalore districts. Depth to water levels of 10 to 20 mbgl
occurs as scattered pockets with larger areal extent in parts of Bidar,
Dharwad, Gadag, Koppal, Haveri, Bellary, Davanagere, Shimoga, Chitradurga,
Tumkur and Kolar districts. This is due to comparatively higher ground
water development in some parts and due to proximity to recharge areas in
other parts. More than 20 mbgl water level is found in very small area of
the state as localised pockets. Annual
Ground Water fluctuations for Pre and Post - Monsoon
: Annual
pre monsoon fluctuations between May 01 and May 2002 analysed for
Karnataka indicates that the rise in water level of 0-2, 2-4 and more than
4 m has been recorded in 22.3%, 3.4% and 2.8% NHNS respectively. Whereas
fall in water level of 0-2, 2-4 and more than 4 m is found in
49.8%, 16.8% and 5% respectively.
During the post monsoon period between Nov, 2001 to Nov, 2002 the
State has recorded a rise in water level of 0-2 and 2-4, and more than 4 m
as 42.8%, 8.3% and 3.5% respectively. Whereas the fall in water level of
0-2, 2-4 and more than 4 m has been recorded as 36.5%, 6.5 % and 2.5%
respectively. Comparison
of pre and post monsoon ground water levels with the mean water levels of
the preceding decade gives a picture of long term change in water levels.
Comparison of mean water level for the period May 92 to May 01 with May
2002 water levels indicates that the rise in water level of 0-2, 2-4 and
more than 4m has been recorded in 52.9%, 13.2% and 5.5% NHNS respectively.
Whereas fall in water level of 0-2, 2-4 and more than 4m is found in
22.1%, 4.8% and 1.4% respectively.
For the post monsoon period comparison of mean water level for the
period Nov. 92 to Nov.01 with Nov. 2002 water levels indicates that the
State has recorded a rise in water level of 0-2 and 2-4, and more than 4m
in 54.0%, 17.6% and 5.9% respectively. Whereas the fall in water level of
0-2, 2-4 and more than 4m has been recorded in 18.1%, 3.2 % and 1.1%
respectively. CHANGE IN
GROUNDWATER LEVEL, May 2002 TO Jan 2003
Water
levels from 680 stations were compared to know the annual change in
groundwater level
in Jan 2003 with that of May 2002. On
the whole 447 wells, amounting to 66% of the analysed wells have recorded
a rise in water level during Jan 2003.
The balance of 223 wells, amounting to 34% have recorded a fall.
In the rise category, the rise of water level in the range 0-2 m is
the most prominent and is observed in 286 wells accounting for 42% of the
analysed wells. Rise in water level in the range of 2 to 4 m. and >4 m. is
recorded in 129 wells (19%) and 32 wells (5%) respectively.
In the fall category, the fall of water level in the range of 0 –
2 m is prominent and is observed in 169 wells accounting for 25 % of
analysed wells. Fall of water
level in the range of 2 to 4 m. and > 4 m are seen in 48 wells (7%) and
16 wells (2%) respectively.
A map depicting the change in groundwater level in January 2003 as
compared to May 2002, showing rise/fall in the ranges of 0 to 2 m, 2 to 4
m and >4 m was prepared (Plate IK). The map
shows that major portions of the state show either a rise or fall in
groundwater level in the range of 0 to 2 m.
Between the two, the ‘rise in water level area of 0 to 2m’ is
more as compared to the ‘fall in water level area of 0 to 2m’
The map shows that rise in Ground Water of 0 to 2m.,is prominent in
northern, southern and western parts of the
state. Parts of Bidar, Gulbarga, Bijapur, Bagalkot, Belgaum,
Bellary, Raichur, N.Kanara, Udupi, Coorg, Shimoga, Dakshina Kannada,
Tumkur, Mysore, Chamarajanagar and Bangalore districts have recorded rise
between 0 to 2 metres. Rise of 2 to 4m, occurs as pockets in parts of
Bidar, Gulbarga, Bijapur, Bagalkot, N.Kanara, D.Kanara, Shimoga and
Chamarajnagar districts. Rise of >4m., is found as very small pockets
in Bidar, Gulbarga, Bijapur,
Bagalkot, Belgaum, Bellary, Raichur, N.Kanara,
Dakshina Kannada, Tumkur, Mysore
and Chamarajanagar districts.
In the fall categories, a fall of 0-2m is prominently observed in
central and Eastern parts of the state covering parts. In the other
parts of the state it was in pockets. Fall of 2 to 4m. occurs as small
pockets in Belgaum, Chikmagulur, Bangalore, Mysore and Coorg Districts.
Fall of >4m., occurs as islands in parts of Belgaum, Chikmagulur,
Bangalore, Mysore and Coorg Districts. CHANGE IN
GROUNDWATER LEVEL, JAN 2002 TO JAN 2003
Water levels from 737 stations were compared to know the annual
change in groundwater level
in January 2003 with that of January 2002.
On the whole 277 wells amounting to 38% of the analysed wells have
recorded a rise in water level during January 2003. The balance, 460 wells
amounting to 62% have recorded a fall. (Annexure II b)
In the rise category, the rise of water level in the range 0-2 m is
observed in 249 wells accounting for 34% of the analysed wells.
Rise in water level in the range of 2 to 4 m. and >4 m. is
recorded in 22 wells (3 %) and 6 wells (1 %) respectively. In the fall
category, the fall of water level in the range of 0 – 2 m is observed in
301 wells accounting for 41 % of analysed wells.
Fall of water level in the range of 2 to 4 m. and > 4 m are seen
in 100 wells (13%) and 59 wells (8 %) respectively.
A map depicting the change in groundwater level in Jan 2003 as
compared to Jan 2002, showing rise/fall in the ranges of 0 to 2 m, 2 to 4
m and >4 m was prepared (Plate IIK). The map
shows that major portions of the state show either a rise or fall in
groundwater level in the range of 0 to 2 m.
Between the two, the ‘fall in water level area of 0 to 2 m’ is
more as compared to the ‘rise in water level area of 0 to 2 m’
The map shows that rise in Ground Water of 0 to 2m. is prominent in
northern and western parts of
the state. The rise is in
isolated pockets in rest of the state. Rise of 0 to 2 metres was recorded
in parts of Bidar, Gulbarga, Belgaum, N.Kanara, Udupi, Coorg, Shimoga,
Dakshina Kannada, Mandya, Davangere, Hassan and Chamarajanagar districts.
Rise of 2 to 4m., occurred as small pockets
in parts of Bidar, Davangere,
Udupi, Hassan and Dakshina
Kannada districts. Rise
of >4m. is found in and
very small pockets in Hassan and Davangere districts.
In the fall categories a fall of 0-2m is prominent in the entire
state except in northwestern parts. Fall of 2-4 metres is observed in
Bijapur, Bagalkot, Gadag, Bellary, Bangalore Chikmagalur, Raichur, Kolar,
Hassan, coorg and Mysore . Fall of >4m. occurs as islands in parts of
Bellary, Chikmagalur, Hassan, Mandya, Kolar, Mysore, Coorg and Chitradurga
districts. CHANGE IN WATER
LEVEL, MEAN (Jan 93 TO Jan 02)-Jan 03
Mean groundwater level for the period Jan 1993 to Jan 2002 was
compared with the groundwater level in Jan 2003. It is seen that out of
the 753 stations compared, 315 stations
accounting for 42 % showed a rise in water level during Jan
2003 as compared to preceding
decadal mean and the remaining 438 wells
or 58 % showed a fall. (Annexure II c)
In the rise category, a rise of 0-2 m is most prominent and is
recorded in 285 stations accounting to 38 % of analysed wells.
A rise of 2-4 m and >4 m is seen in 26 wells (3 %) and 4 wells
(1%) respectively. In the
fall category, a fall of 0 – 2 m is the most prominent and is recorded
in 281 wells accounting to 37% of analysed wells.
Fall of 2 to 4 m and >4 m is seen in 108 wells (14%) and 49
wells (7%) respectively.
A map showing the change in water levels as described above,
showing rise/fall in the ranges of 0-2 m, 2-4 m and >4 m was prepared
(Plate – IIIK). The map
shows that parts of northeastern, coastal, southern
and malnads have shown a rise. A rise of 0-2m is most prominent and
is found to occur in Gulbarga, Raichur, Bellary, Tumkur, Bidar,
D.Kanara, Chikmagulur, Udupi Shimoga, N.Kanara, Mandya, Hassan,
Chamarajangar and Bagalkot.
Rise of 2 to 4 m occurs as small pockets. Rise of >4 m., occurs as
small localized patches in parts of Hassan and Bidar
district.
In the fall categories, fall of 0-2m. is prominently seen in parts
of Bidar, Bijapur, Bagalkot, Belgaum,
N.Kanara, Shimoga, Mandya, Mysore, Hassan, Dharwar, Chamarajanagar, Haveri,
Gadag, Koppal, Chitradurga, Chikmagalur, Bangalore, Coorg, Udipi, Mysore, Davangere and Kolar districts. Fall of 2 to 4m. occurs in
Bidar, Bijapur, Bagalkot, Belgaum, N.Kanara, Shimoga, Mandya, Mysore, Hassan,
Chamarajanagar, Haveri, Gadag, Koppal, Chitradurga, Chikmagalur, Bangalore,
Coorg, Udipi, Mysore, and
Kolar districts. . Fall of
>4m., was noted in Dharwar, Belgaum, Haveri, Coorg, Bangalore and Kolar
mostly localised in nature.
DEPTH
TO WATER LEVEL Jan 2003
The depth to water level recorded in the state ranged from 0.32
mbgl (Belgaum district) to 26.05 mbgl
(Chikmagulur district). It is seen that out of 782 stations
monitored during the month, 6 % wells have less than 2 mbgl water level,
27 % wells have 2 to 5 mbgl water level and 51 % wells have 5 to 10 mbgl
water level. Thus, about 84 %
of the analysed wells have water level within 10 mbgl.
Moderately deep water levels of
10 to 20 mbgl are seen in 15 % wells and deep water levels of > 20 m is
found in about 1% of the analysed wells. ( Annexure
III )
A map showing the depth to water level in the ranges of <2,
2to5, 5to10, 10to20 and >20mbgl was prepared (Plate IVK).
The map shows that major portion of the state is having a water
level of 5 to 10 mbgl, followed respectively by 10 to 20 mbgl and 2 to 5
mbgl water levels. Depth to water level of <2 mbgl and >20 mbgl
occupy very small areas. It is seen from the map that water level of 5 to
10 mbgl is generally found throughout the state occupying parts of most of
the districts. Water level of 10 to 20 mbgl is also found in almost all
the districts and is prominently seen in the central and southern parts of
the state. 2 to 5 mbgl water level is found as small pockets scattered all
over the state with larger areal extent in parts of Gulbarga, Raichur,
Bellary, N.Kanara, Udipi, S.Kanara, Coorg, Chikmagalur, Shimoga, Mandya,
Chamarajanagar and Bangalore districts. >20 mbgl water level is found
as very small pockets in parts of Dharwar, Koppal
Bagalkot and Gadag districts. 3.2.
Goa:
The
details of network observation stations, which are being, monitored in Goa
state is shown in table 7. During the premonsoon (May) period depth to
water level ranges from 1.00 to 18.92 mbgl. In general depth to water
level between 2 and 5m in 6 taluks of North Goa district and 2 taluks of
South Goa district.
Depth to water in the range of 5 to 10m is observed in Satari taluk
and as isolated patches in 3 taluks. Deep water levels in the range of
10-20m are observed as patches at Satari, Sanguem, Canacona ,and Quepem
and Pernem taluks. The shallow ground water levels of 2 to 5m is observed
in majority area in Pernem, Bardes, Bicholim, Satari, Tiswadi and Ponda
taluks in North Goa district and Marmugoa, Salcete, Quepem and Canacona
taluks of South Goa district. Less than 2m ground water level is observed
in parts of Pernem, Tiswadi taluks of North Goa district and parts of
Canacona, Quepem, Sanguem taluks of South Goa district. Ground
water fluctuation scenario between May and November : The
rise in ground water level varied from 0.12 to 7.06 m and from 0.08 to
2.80 m in South Goa and North Goa respectively. The decline in ground
water level varied from –0.2 to –3.71m and from less than one meter to
–5.50m in South Goa and North Goa districts respectively. The rise and
fall of less than one metre to 2m is observed in most part of the state,
The rise and fall of more than 4m is observed in Salute and Sanguem taluks
of South Goa district and Tiswadi taluk of North Goa district
respectively.
Table 7: District wise distribution of NHNS in Goa
4.
HYDROCHEMICAL ANALYSIS, REMOTE SENSING , GEOPHYSICAL AND
HYDROMETEROLOGICAL STUDIES a)
Hydrochemical analysis:
In the regional chemical laboratory of SWR, a
total of 12873 water samples were analysed between 1992 - 2001. The
details are presented in table.8 both for Karnataka and Goa. Based on the
Chemical analysis of water samples, following reports and maps were
prepared. *
Water quality maps/Reports *
Ground Water Yearbook showing distribution of electrical
conductivity. *
Chemical Analysis Data up to 1998 has been computerised. Interpretation
of chemical quality of ground water: For the assessment of general ground
water quality ground water samples collected from Hydrograph stations /
Systematic and Reappraisal surveys / Exploratory well programme /
Hydrology Project (HP) /Special studies/ etc have been analysed for
parameters such as EC, Cl, SO4, NO3 and F apart from
other parameters like Na, K, Mg,and Hardness etc. The results are grouped
into three categories corresponding to Bureau of Indian Standards for
drinking water (1991) vis-a-vis desirable, permissible and unsuitable
category. The chemical analysis carried out for various samples reveal
that by and large ground water quality of Karnataka and Goa states are
suitable for drinking / domestic purposes except in some industrial
pockets where high nitrate content is reported. Table.8 Status of hydrochemical analysis
b)
Remote Sensing studies As
a part of resource evaluation studies and as additional input for
hydrogeological surveys, studies are undertaken using air
photos and land sat imageries. Besides utilising them in exploratory
drilling programme, Remote sensing studies have also been
used in delineating potential zones in respect of drought
prone districts of Chitradurga, Dharwar, Kolar, Bangalore, Tumkur,
Gulbarga, Belgaum, and Raichur districts and tribal
districts of Dakshina Kannada
and Kodagu. Visual interpretation of the
imagery and Digital analysis were also carried out in parts of
Raichur district under application validation programme with Department of
Space. As
a part of MOU with NRSA, Hyderabad, Central Ground Water Board was
involved into the quality check evaluation of the Ground Water Prospects
Maps under Rajiv Ghandhi Drinking Water Mission with State Remote Sensing
Cell. Govt.of Karnataka. c)
Hydrometerological studies Monthly
and annual rainfall data for the raingauges located at the headquarters of
the 175 taluks are collected, compiled and stored in the rainfall data
base file. This database file
is part of the Hydrometerological Information System, developed and being
used in this region. This
software facilitates consist of retrieval of data in the desired format.
Statistical analysis and averages based on polygons can also be computed. Rainfall data from 1901 to 1998 is available in the database.
Under experimental artificial recharge studies in Kolar district, analysed
and computed tank water balance and stream flows pertaining to
Gauribidanur and Mulbagal taluks. A weather station which was established
during the course of VRBP was continued till 1988, wherein all the
parameters such as rain fall intensity, evaporation, wind
velocity, humidity, max.- min.temperature, sunshine hours
were recorded daily. Information collected is analysed for
estimating the water surplus from rainfall and is correlated to the
rise in ground water level recorded in the area. Rain gauge
station has also been established in Bidadi watershed in Bangalore
district. Software
developed in dBase III plus and Fox plus in association with
National Informatics Center. Work is also in progress for
computer based data management system for the data generated during
hydrogeological surveys and exploratory drilling. d) Geophysical Surveys: Geophysical
survey both surface and well logging are taken up as a part of ground
water exploration programme. Surface studies are also taken up in
connection with Water supply investigations for pinpointing sites
where drilling can be taken up. Geophysical
logging helps in delineating the fractures encountered in
the bore holes and is also utilised in designing the wells in
coastal alluvium, where quality variations of the formation
water are noticed. Geophysical
surveys in Karnataka comprising Vertical Electrical Sounding
(VES), Resistivity profiling and VLF surveys were conducted
in different parts of the state to *
Estimate the thickness of the aquifers *
Estimate overburden thickness. *
Delineate sheared and fractured rocks *
Locate structures like dykes, Faults etc. which control the
Ground water movement. *
Study the relative variation of the Quality of Ground water.
3190
VES, Resistivity/VLF profiling for a length of 27.15-line km were carried
out. Based on the results, suitable recommendations were communicated
for taking up drilling. Geophysical
logging is carried out in the state in 117 bore wells in the depth range
of 70.0 - 300 meters. The logging comprises recording of Self Potential
(SP), Point resistance (PR), N 16" & 64"normal resistivity
and lateral receptivity using lateral log and gamma activity. 5.
GROUND WATER RESOURCE ESTIMATION
The
recharge to ground water is mainly through precipitation, apart from other
sources like return flow from applied
irrigation, tanks etc. The
state predominantly underlain by the hard rock aquifers, which responds
quickly to the rainfall and starts building up of the water levels. During
the summer period the depth to water shows falling trend with appreciable
dwindling of resources
and fall in discharge of wells. a).
Ground Water Resources availability in Karnataka. The
total replenishable ground water of Karnataka as per ground water
estimation committee methodology (1984) is estimated as on March’92 as
1.6175 million hectare metres (Mha.m) and out of this 0.2418 Mha.m has
been kept for domestic and industrial uses.
The district wise ground water availability and potential created
upto 1998 along with balance available for development has been given in
the table 9. Out of the 175 taluks/blocks, 6 taluks are over exploited and
8 taluks fall in dark category and 13 taluks fall in the grey category
(table.10). The
estimated utilisable irrigation potential from ground water is 2.44268
million hectares and as on March’98 about 0.80608 million hectares had
been developed and an area of 1.63660 million hectares are still to be
developed. TABLE
9 : Ground Water
Resources and Irrigation potential of Karnataka as
on March 1998.
1 - Serial Number
2 - Districts 3 - Annual Natural Recharge (Mha. M) 4
- Provision for drinking and industrial use (Mha. M) 5 - Available recharge (Mha. M) 6 - Utilisable recharge (Mha. M) 7 - Net draft (Mha. M) 8 - Balance GW available (D-E) in Mha. M 9 - Utilisable irrigation potential for development (Mha) 10
– Stage of development in percentage. Table.10:
Grey (Semi-Critical), Dark (Critical) and Over- Exploited blocks in Karnataka
(As on March 1998-Provisional)
b).
Ground water resource availability in Goa.
The estimated utilisable ground water resource of the state is in
the order of 165 MCM and the net draft projected up to March 1998 is 16
MCM. The balance ground water resource for future development is 149 MCM.
The stage of Ground Water development is less than 10 percent except in
Ponda and Tiswadi taluks where it is 15 % and 14 % respectively. In
Canacona taluk, the stage of development is 31 %. 6.
SPECIAL STUDIES : a) Experimental
Artificial Recharge Studies in Kolar District, Karnataka. Ground
water irrigation has gained importance during the last decade in Karnataka
through dugwells, dug-cum-borewells and borewells in some districts,
especially in areas where perennial rivers are absent.
Kolar is one among such districts
which has experienced high stage of ground water development where a spurt
in groundwater activity is seen during the past two decades.
The periodical monitoring of wells for the period 1973 to 1996
shows a declining trend in ground water levels.
The area showing declining trend in ground water levels are
associated with higher degree of ground water development. Central
ground water Board under Central Sector scheme has initiated Experimental
Artificial Recharge Studies (EARS) in Gauribidanur and Mulbagal taluks
during 1993-94 and continued in the subsequent years. The
main activities are : Desilting
of two tanks, one each in Gauribidanur and Mulbagal taluks and converting
the same into Percolation tanks. Watershed
treatment in two areas Construction
of point recharge structures (5). Gravity
recharge wells.(2) Roof
top rain water harvesting structure at Gauribidanur. Construction
of Percolation Tanks: The
existing defunct and silted up M.I. tanks at Errapothenahalli and
Manchiganahalli were taken up for conversion to percolation tank after
desilting. Government of
Karnataka had plans to take up desilting of M.I. tanks in Kolar district
on a large scale and in this context the district level authorities
emphasized the need to quantify the additional recharge through such
desilting programme. Keeping
this in mind, it was planned to take up study of the tank bed seepage
prior to desilting and after desilting and thereby quantifying the same. Watershed
Treatment : Treatment
of Basavapura and Bhovibikkanahalli micro-watersheds with traditional
water harvesting structures to study the impact
the same on ground water recharge.
The studies were taken up as watershed development programme, which
are being taken up in Karnataka on a large scale and the present study
attempts to quantify the additional recharge by such programmes. Check
dams are the major structures constructed under this programme. Point
Recharge Structure (PRS) Findings
of Artificial Recharge Studies: Percolation
tanks : Infiltration
tests results carried out at Percolation tank beds prior to and after
desilting showed an improvement in tank bed percolation. The infiltration
rate ranged from 0.17 to 2.4 cm/hr prior to desilting whereas the rate has
increased in the range of 1.8 to 8.8 cm/hr after desilting at
Errapothenahalli. At
Manchiganahalli, it ranged from 1.2 to 5.8 cm/hr prior to desilting
whereas the same was observed to be in the range of 10 to 16.8 cm/hr after
desilting. The ground water level data during post desilting periods
reveals a built-up in storage in the order of 2 to 4.5 m to the downstream
of the tanks. Watershed
treatment : It
has revealed that the flow recorded is considerably reduced after the
treatment and the construction of the structures.
A built-up in storage was observed to be in the order of 3 to 5 m
in the phreatic zone. The treatment of Basavapura
microwatershed has shown watershed treatment can arrest flows
during monsoon and enhance recharge to ground water.
This indicates that watershed
treatment especially in the drought prone district of Karnataka can be
taken up on a large scale which
can contribute greatly to recharging of ground water and retention of
moisture for crop production. Point
recharge structure : The
recharge through point recharge structure has benefited the deeper aquifer
to build-up storage locally and to improve the ground water potential and
are effective in recharging deeper aquifer and can be applied in feasible
areas of a drought prone district. Gravity
recharge experiments: The
experiments carried out at Belchikkanahalli and at Hussainpura have
indicated 3 to 4 lps intake of the aquifer (weathered and fractured
granite gneisses) with a possibility of creating additional storage using
the excess water available in Bandihalla. This can be adopted successfully
in similar environs having surplus source water.
The source water has to be clear and silt free before recharge.
Stream flow and tank water are ideal
as source water. (b)
Artificial Recharge studies in Jnanabharathi campus, Bangalore University: Under
Central Sector Scheme, a scheme on artificial recharge to ground water is
being executed in
Jnanabharathi campus, Bangalore University which cover an area of about
one sq.km. The scheme on completion would harness 0.043 MCM (43,000 m3)
monsoon run-off going as waste and can improve
ground water levels and sustainability of abstraction structures in
the area through artificial recharge structures such as Check dams and
subsurface dyke. This scheme is only
a beginning in the University campus and all the plans are on the
advanced stage to launch a model environmental eco-park in association
with the University. The
salient features of the scheme are:
Total
water available for recharge : 43290 cu.m The
benefits include direct and indirect in any concerned artificial
recharge schemes. An attempt is made to harness the natural surface water
run-off (43290 cu.m) to
recharge the aquifer system instead letting it into a
drainage course. This will help
to maintain the productivity of the existing water supply borewells which
supplies water to the University and Sports Authority of India campus.
The scheme after completion is likely to recharge about 21645 cu.m
(50 percent of 43290 cu.m) of potable water into the depleting aquifer
system in the area. Considering 20 years span of life for the structures,
the annual investment with 10 percent rate of interest works out to rupees
80740. The cost per thousand liters of water harvesting works out to about
two rupees. In addition to above, the possible intrusion of
polluted Vrishabhavati water to the aquifer in the area will be
prevented.
An amount of Rs.13.75 lakhs was sanctioned for the scheme.
Execution of the recharge structures were completed. c)
Conjunctive Use Studies In Ghataprabha River Basin. Conjunctive
use study of surface and ground water in Ghataprabha river basin in parts
of Belgaum and Bijapur districts has been carried out covering an area of
10,370Km2. The
data from CGWB and state agency have been utilised in this study. Ground
water modelling studies were also undertaken during the project period. The
study indicated that canal water utilisation in the left banks command is
1114 MCM and the total water utilisation is 2070 MCM leaving a balance of
1015 MCM for further use one of which 529 MCM is surface water. By increasing the cropping intensity a conjunctive use plan
can be drawn. Non utilisation of ground water in upper reaches of the
basin has resulted the
water logging condition. In
tail end area water deficit is experienced.
A
conjunctive use plan has been drawn both for left and right
bank canal command areas with optimal utilisation of surface and
ground water. Under this a suggestion put forth for left bank canal is that
utilisation of surface water to a tune of 1068 MCM (84%) and ground water
to a tune of 173 MCM (16%) can boost up the cropping intensity to 200%
likewise in the case of right bank canal a cropping intensity of 140% has
been suggested by utilising surface water to a tune of
712 MCM and ground water to a tune of 223 MCM. A
total investment of Rs 40.5 crores has been suggested for construction of
20,691 borewells upto a depth of 80m covering 10 taluks of Belgaum
and Bijapur districts. The main crops suggested for the cultivation under the
conjunctive use plan are Sugarcane, Cotton, Groundnut, Maize and Pulses. d)
Pollution Studies: An
area about 50 sq.km in and around Bhadravathi town in Shimoga
district was studied to assess the ground water
quality and aquifer material vis-a -vis the industries
existing, agricultural practices and urbanisation. The area is
drained by the perennial Bhadra
river and the major industries are M/s Mysore
paper mill and M/s Visweshwariyah Iron and Steel limited. The
area falls in southern transition agroclimatic
zone and receives a mean annual rainfall of 826.3 mm.
Extensive irrigation from Bhadra reservoir and Gondi channel, which
are constructed across the river bhadra is practiced around
Bhadravthi. Premonsoon survey was carried out in June, 1994 during
which 26 dug wells and 17 bore wells were
identified for water level monitoring and sample
collection. Solely granites underlie the area. The premonsoon water
levels ranged from 1.54 to 13.21 mbgl and post monsoon water
levels ranged from 1.16 to 9.88 mbgl and the seasonal fluctuation
(1994-95) ranged from 0.16 to 5.60 m. A
total of 44 water samples, 20 no from dugwells, 21 from bore
wells, 2 from Bhadra river and 1 from municipal water supply in
two sets were collected during pre-monsoon 1994. One
set was analysed in SWR office for 13 parameters and the
other set has been sent to Kerala region,
CGWB,Trivandrum for heavy metal analysis. During
post monsoon 1994, a total of 47 water samples were collected
in 3 sets. Sources of sampling was 21 from dugwells, 18
from bore wells, 2 from river Bhadra, 1 from Municipal
water supply, 1 from canal and 4 no.s from effluent samples. One set
of samples were analysed in SWR office, one set was sent to Kerala
region, Trivendrum for heavy metal analysis and third set
was submitted to Sriram institute for industrial research, Bangalore
for analysing selected parameters. The
key wells were got surveyed to determine (1)reduced levels of
ground water levels to know flow direction and (2) to establish
the relationship of river Bhadra with the ground water in
the area. The study shows that elevation of W.T lies between 565 to
611 m above sea level and the river Bhadra in this section is
effluent in nature and receives water from surrounding
ground water reservoir. In
addition to the above Ground Water pollution studies were carried out in
Mangalore city industrial pockets in Baikampadi area including land fills
study in Mangalore town, industrial town limit of Dvanagere Municipality
around industrial establishment, Industrial pockets around Banglore Metro
area etc., Apart from this inland salinity and Coastal salinity in
parts of Dharwar and Udupi districts were carried out by the Board. 7.
ASSISTANCE TO STATE GOVERNMENT AND SEMI GOVERNMENT ORGANISATIONS,
PUBLIC SECTOR UNDERTAKINGS INCLUDING TECHNOLOGY MISSION FOR RURAL WATER
SUPPLY
Under Technology mission for rural water supply, investigation
to locate source point for 365 identified problem villages in
Gulbarga district, 107 in Dharwar and 76 in Raichur districts
were completed. Other than technology mission source finding in
hardcore/problematic villages were taken in the areas of
investigation. So far 406 villages were covered.
In addition accorded technical clearance in 13
villages for construction of nalla and contour bunds and
recommended sites for 6 villages for water conservation
work under Jawahar Rozgar Yojana in mini mission
areas in Raichur district. Coordinated with various state Govt.
agencies in formulation of schemes, projects etc. 8.
URBAN HYDROGEOLOGICAL STUDY
Urban
Hydrogeological study has been taken up in Bangalore Metro area,
Hubli-Dharwar coporation, Mysore city corporation and Mangalore city
corporation. 8.
HYDROLOGY PROJECT Under
the World Bank assisted hydrology Project constructed
piezometers for continuous monitoring of ground water levels
using digital water level recorders were taken up. CGWB along with
MGD, Govt.of Karnataka have drawn a plan to construct 805
Piezometers in Karnataka. The CGWB participation involves analysis
of NHS for water level and water quality data. The
basis for selection of sites for the piezometers
construction is as follows. a.
Topography b.
Hydrogeological condition c.
Optimisation study for PZ density location d.
Depth of existing NHS location e.
Water level changes over a period of time. f.
Dark and grey blocks g.
Agroclimatic conditions. h.
Quality considerations in respect of fluoride and nitrate. Based
on the analysis of historical data of water levels the optimum
number of observation station decided for CGWB in Karnataka is
310. In Karnataka, under Hydrology Project, 367 piezometers were
constructed. 9.
PREPARATION AND ISSUANCE OF VARIOUS
REPORTS AND MAPS. (i)
Reports summarising the results of investigations
for all the districts (ii)
Action plan for development of Ground water in drought prone
districts of Dharwar, Kolar, Bangalore, Belgaum, Bijapur,
Raichur, Bidar, Tumkur, Gulbarga, Chitradurga, Bellary, Mandya,
and Tribal districts of South Kanara,
and Kodagu (iii)
Basin reports for
West flowing river, Malaprabha river, Cauvery and Palar
river (iv)
Hydrogeological conditions in the state (v)
Report detailing the master plan for the development of
ground water (vi)
Geophysical survey report pertaining to Raichur and Kolar districts
(vii)
Action plan for augmentation of Artificial Recharge
studies in Devanahalli/Hoskote taluks of Bangalore district (viii)
Silver jubilee report of NHS in Karnataka (ix)
Ground water Atlas Karnataka (x)
Hydrogeological and reappraisal survey reports (xi)
Water supply investigation reports (xii)
Basic data reports of exploratory
borewells drilled under VRBP and
Southwestern region and Goa (xiii)
State report (revised) incorporating network stations
data upto 1999 (xiv)
Decennial report titled "Behaviour of Ground
water levels and quality in Karnataka 1979-88" (xv)
Karanataka atlas (xvi)
Master plan of Goa (xvii)
Exploration report of Karnataka and Goa. (xviii)
Report on experimental artificial recharge studies, Kolar district. (xix)
Ground Water year books. 10.
HIGHLIGHTS v
The Canadian
Assisted Ground water project studies carried out in Gulbarga and
Bidar districts have indicated feasibility for sinking 980
additional borewells of which 57 wells are in granitic terrain
and 923 wells are in basaltic terrain capable
of creating an additional irrigation potential of about 2500 ha. v
The project studies
in Vedavathi River Basin have revealed the exploitable ground water
reserve of the order of 1948 MCM.This would support an
additional number of 30,000 wells.The optimum depth for the
dug cam bore wells and bore wells have been worked out to be 30 - 40
metres and 50- 60 meters respectively. The feasible areas for the
additional wells have been delineated in which well siting has to be
done on scientific basis considering the complex hydrogeological set up
of the project areas. The sea pumping rate of different
areas have been worked out. An additional area of
1,00,000 ha. can be brought under irrigation through the above
additional wells. v
In the Kaladgi
formations dug wells are appropriate except in the Karstified(Cavernous)
limestone as in Lokapur - Bagalkot valley (Bijapur
district). These horizontally bedded formations are poor
aquifers and bore wells are found to be failure. Areas feasible
for high capacity bore wells (over 30000 lph) have been
demarcated in parts of Bagalkot, Bilgi,
Badami, and Mudhol taluks. Also Borewells are more
suitable in the proved tectonic
zones to tap the deeper aquifers. Shallow tube wells are feasible in
Kulgeri - Badami valley along the abandoned channels. v
In Bhima
basin ground water development should be confined chiefly
to the disturbed zone by means of borewells and dug cum bore
wells. v
Brochures and
attributes on ground water in local langauage (kannada) were prepared and
distributed to various state agencies during mass Awareness Programmes
held at various taluks/district head quarters and filed areas. v
Work shop organised
under Hydrology project for transfer of Technology. v
Officers got
training at different occasions in various disciplines like hydrogeology,
hydrochemistry and remote sensing , geophysics, computers etc. v
Induction leveL
Training programme was conducted at Bangalore during 2001-02.
Annexure-II
Status
of function of Chemical instruments in South Western Regional Office
Annexure-III
Status
of function of Geophysical instruments in South Western Regional Office
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