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Over the
last 20 years there has been an enormous increase in the use
of ground water resources all over the world. Besides
providing an important source of water for domestic and
agricultural use, groundwater also plays a key role in
supporting and maintaining the livelihoods of the poor. This
is because groundwater can be accessed relatively easily and
cheaply and its quality is generally high. The intensity of
groundwater exploitation has raised concerns that groundwater
use and the livelihoods it supports - may not be sustainable.
Symptoms of over-exploitation include declining water levels
and increasing competition between users for scarce supplies.
Now a days due to over exploitation of ground water for
irrigation purposes, the water table is falling by about 20-25
cm per year in good ground water quality regions of Punjab,
Haryana & Gujarat (Source: CGWB). Therefore there is urgent
need for recharging of groundwater resources.
Artificial
Recharge
Artificial recharge is an important aspect of groundwater
management as it provides storage space free of cost avoids
evaporation losses and allows use of stored water during dry
period. Artificial recharge is achieved by three methods,
namely by:
1. Spreading
2. By induced recharge and
3. By injection
The suitability
of a particular method is based on the hydro geological
conditions, quality of source water and proposed use of
recharged water. These methods are explained below:
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1.Spreading Methods:
This method is similar to that of surface
irrigation with the difference that in recharge operation the
water is allowed to stand on the field for a much longer
period. The following three aspects should be considered for
spreading methods as shown in Fig1.
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Fig1 :
Showing Infiltration-Recharge System |
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·
Getting the
water into the ground.
·
Getting the
water down through
the vadose zone to the aquifer.
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· Getting
the water to move through the aquifer away from the
infiltration site without undue build-up of groundwater mounds.
Thus,
for successful infiltration of recharge systems, the following
conditions are desirable:
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Fig2 :
Showing Perched Ground Water above
Clay Layer in Vadose Zone. |
· Surface soils
must be sufficiently
permeable to maintain high infiltration rates.
·
Vadose zones must be permeable and free from clay layers or other finer materials that could restrict downward
flow of water and produce perched groundwater (See Fig.2) that could back up into infiltration basins.
· Aquifers
must be unconfined and
permeable and thick enough to avoid excessive rise of groundwater mounds.
·
Groundwater tables must be deep
enough to allow some rise in the water table, or the
water table must be controlled with wells or drains that take
the recharge water out of the aquifer again. |
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Keeping in view the above-mentioned conditions and hydro
geological set-up of Punjab State, the following areas offer
suitable conditions:
-
Kandi belt
adjoining the Shivalik system where alluvial plains exist.
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Area of old
river courses, which can be identified with the help of
Landsat data.
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Areas around
flood plains (in and along stream beds).
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Areas
different than the above three categories and where
unconfined aquifers predominate.
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In all the
four categories, sometimes, sandy soils at top may be
covered by clay or other fine textural material. This
situation occurs in flood plains or other alluvial
deposits. In case the layer of fine top materials is not
too thick, it can be removed and the infiltration basins
can be excavated into the coarse underlying deposits as
shown in figure 3. Surface soils also play an important
role in controlling the infiltration rates.
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Fig3 :
Showing infiltration Basin excavated through Clay to
Underlying Sand |
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According to
size soils are classified as clay (<2 microns), silt (2-50
microns), and sand (0.05-2 millimeters). Particles larger
than 2 mm in diameter are classified as gravel (fine, coarse,
cobbles, and boulders). Usually infiltration basin soils
should be sandy loams or coarser to produce acceptable
infiltration rates (for example, more than 20 cm/day). Coarse
sands and gravels can give very high infiltration rates.
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Table: Showing Soil Texture and Estimated Rate of Infiltration
(Modified after Todd, 1985)
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Infiltration
Rate
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Soil Texture
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High
(Greater than 5cm/hr)
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Coarse sand,
sand, fine sand, loamy sand, loamy fine sand, coarse sandy
loam.
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Intermediate
(Between 5 cm/hr and 1.5 cm/hr)
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Sandy loam,
fine sandy loam.
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Low
(Less than 1.5 cm/hr)
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Silt loam,
sandy clay loam, clay loam, Silty clay, sandy clay, clay.
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Methods of water spreading involve:
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Construction
of Basins
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Stream
channels
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Ditch and
furrows
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Flooding
-
Irrigation
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Pits and
shafts
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These methods
have been discussed below in relation to their utility for
Punjab State
Basin Method:
In
this method, basins are constructed by excavation or by
building dikes or levees. Sizes and shapes are adjusted to
fit topography, land ownership and available land. Depending
on topography, basins can have a surface area of 0.1 hac (0.25
acre) or less to 10 hac (25 acres) or more. Often, the first
few basins are "sacrificed" as presedimentation facilities.
Water is then released to basins for infiltration. Water
released should have minimum sediment load so to reduce
deposition and scaling of basin surfaces. This can be
accomplished by three ways:
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Diverting
water to basins during non-flood periods when suspended
sediment is low.
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Adding
chemical flocculating agents to water to remove sediment.
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Providing
sedimentation basins to hold water before releasing it into
recharge basins.
Basin designs
vary widely depending upon local conditions. Basin width
should be sufficiently wide to accommodate scrappers to remove
sediment periodically. Side slopes should be relatively steep
so as to minimize sediment deposition.
In actual infiltration basins, suspended material in the water
(silt, clay, organic particles, etc.) accumulates on the
bottom. Also bacterial and algae growth in the basins
produces algae crests and organic deposits on the bottom.
These accumulations reduce infiltration rates, typically if
the water contains high suspended solids content and the
basins are flooded for a long time. Thus, the hydraulic
conductivity 'K' of the bottom soil gives an idea of maximum
sustained infiltration rates in the basin. Order of magnitude
of hydraulic conductivity K for different soils are (in
m/day):
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Clay soils
(surface)
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0.01 -0.2
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Deep clay
deposits
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10-8
- 10-2
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Loam soils
(surface)
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0.1 - 1
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Fine sand
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1 - 5
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Medium sand
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5 - 20
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Coarse sand
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20 - 100
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Gravel
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10 - 1000
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Sand and
gravel mixes
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5 - 100
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Clay, sand
and gravel mixes
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0.0001 - 0.1
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These values give a general idea of K-ranges for different
soils, hence, of the maximum infiltration that can be obtained
to get more reliable estimates. In Punjab infiltration basins
can be constructed close to rivers, and in areas of old river
courses, and in wide channels. Studies by Central Ground
Water Board have shown that basins of 250 m X 60 m size and
having depth of 2 m to 5 m can be constructed to carry
artificial recharge. |
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Stream Channel Method:
Water spreading in stream channels involves operations to
increase the time and area of water contact. Activities
typically require upstream storage facilities to regulate
stream flows and channel modifications to enhance
infiltration. Ideally, upstream reservoirs should limit flows
to rates that do not exceed the absorptive capacity to
downstream channels. Types of stream channel
improvements include:
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Widening
leveling, scarifying or ditching of the channel.
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Permanent low check dams, which do not cause flood hazard.
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Temporary low check dams consisting of stream bed materials.
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L shaped
finger levees constructed by bulldozer at the end of
high-stream flow season.
In
Punjab, this method is particularly suitable for Kandi area of
District Ropar, Hoshiarpur, and Gurdaspur.
Ditch and Furrow
Method:
In this method continuous ditches and furrows are
constructed throughout the field, which facilitates the
infiltration rate by providing more surface area. Ditches and
furrows are adaptable to irregular terrain where other methods
of water spreading would not be feasible. This method is not
suitable for Punjab State and is mainly practicized in hilly
regions with uneven topography.
Flooding Method:
In flat land areas, water can be simply released
over large area and allowed to infiltrate. Velocities of flow
should be minimal to avoid soil movement. Usual practice is
to leave vegetation of that area undisturbed. This method is
the least costly of all spreading methods, provided the land
is available without cost. For maximum efficiency, hard labour should be employed to distribute the water over area as
wide as possible. This method has very limited scope in a
state like Punjab where most of land is cultivated.
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Irrigation Method:
Water can be recharged on irrigated lands by three methods:
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Applying
excess water during non-irrigation seasons.
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Applying
excess water during irrigation (However, this can have
adverse effects on leaching salts and removing soil
nutrients).
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Keeping
irrigation canals full .
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This method is
also not suitable to the conditions of Punjab except in last
option i.e. keeping the irrigation canals full in central
parts of Punjab having sweet water (District Ludhiana,
Jalandhar, Kapurthala, Amritsar, Gurdaspur). However, canal
network is very little in Bist Doab Tract (Ludhiana,
Hoshiarpur, Jalandhar). As such this method has also very
little scope in Punjab.
Pit Method:
Pits are
excavated into permeable formations, which serve as ideal
facilities for artificial recharge. Abandoned gravel pits are
most economical for this purpose. This method has also very
little application in Punjab.
Induced
Recharge:
Induced recharge
occurs where groundwater is pumped from a location near a
surface water body so that lowering of groundwater level
induces water to enter the ground from the surface source.

Fig 4 :
Showing flow pattern with pumping well |
The method
is effective in permeable formations, which hydraulically
connected between the stream and the aquifer (See Fig.4).
The amount of water depends on: pumping rate,
permeability, type of well, distance from stream and
natural groundwater movement. The stream velocity should
be sufficient to prevent sediment deposition from sealing
the streambed. |
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Injection Methods: Such methods are of particular interest where
over drafting occurs in confined aquifers and areas are
located close to major canals. As water is available
during monsoons, injection methods are suitable on account
of clean waters available close to sites (See Fig.5).
Such methods can be tried areas having confined aquifers
and suffering from over drafting of groundwater. |
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Other Measures:
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The other
measures aim at reducing the ground water overdraft. It is
suggested that in severely over draft areas, new cropping
patterns may be introduced. Crops, which require less water
than the existing crops, shall have to be promoted. e.g.
wheat Rice-Rotation practice should be replaced in Punjab
and Haryana as early as possible.
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In critical
areas, legislative measures can be introduced. Pumping
patterns can be regulated keeping in view the available
water supply in the canals.
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There is need
to educate the farmers regarding optimum water utilization
aspects, irrigation planning etc. Public awareness
regarding water conservation measures should be created
through Celebration of 'National Water Day' and with the
help of awareness programmes through people's participation
and voluntary organizations.
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Recycling of
water and reuse of water should be promoted especially in
those areas where industries consume groundwater.
By utilizing one
or a combination of above-mentioned methods depending on its
suitability to a particular area we can regenerate our
groundwater resources to a great extent.
Source:
Summarized from DFID News-Letter & Technical Report on
Water Management by Punjab Irrigation Department.
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