Ecorestoration of Banni Grassland - Global Restoration Network
Ecorestoration of Banni Grassland - Global Restoration Network
Ecorestoration of Banni Grassland - Global Restoration Network
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<strong>Ecorestoration</strong> <strong>of</strong><br />
<strong>Banni</strong> <strong>Grassland</strong><br />
rainfall. Further, due to selling <strong>of</strong> cow dung from<br />
<strong>Banni</strong>, the natural supply <strong>of</strong> manure has been considerably<br />
reduced. It has been reported that, about<br />
a ton <strong>of</strong> cow dung consists <strong>of</strong> 75 per cent water and<br />
remaining consists <strong>of</strong> 4.5 kg nitrogen, 2.3 kg phosphoric<br />
acid and 4.5 kg potash and that the cattle<br />
returns nearly 75 per cent nitrogen, 80 per cent phosphoric<br />
acid and 90 per cent potash obtained from<br />
her feed (Owen 1980). The two-way system; intake<br />
<strong>of</strong> nutrients through grass feed and its release<br />
through dung facilitate almost no loss or negligible<br />
loss <strong>of</strong> nutrients from the grassland area. However,<br />
the disruption <strong>of</strong> this cycle, through selling <strong>of</strong> cow<br />
dung, in <strong>Banni</strong>, has gradually affected the soil nutrients<br />
<strong>of</strong> the area, which in turn has affected plant<br />
growth. Therefore, to increase the soil nutrients <strong>of</strong><br />
the restoration site, farmyard manure was added at<br />
the rate <strong>of</strong> 2 tonnes per ha. This, apart from improving<br />
the nutrient status <strong>of</strong> the degraded land would<br />
improve the physical properties <strong>of</strong> the soil such as<br />
permeability, soil structure etc. Also, the chemical<br />
binding <strong>of</strong> dung with that <strong>of</strong> soil is known to reduce<br />
the soil salinity to some extent.<br />
3.5 Legume Introduction<br />
Grass-legume mixtures are always desirable because<br />
<strong>of</strong> their complementary functions in providing nutritive<br />
and palatable forage for livestock. Legumes<br />
usually maintain their quality better than non-legumes<br />
even at maturity and being rich in protein<br />
they enhance the forage value and also add substantially<br />
the needed nitrogen to the soil. Thus,<br />
grasses are directly or indirectly benefited by the<br />
use <strong>of</strong> nitrogen components manufactured by the<br />
legumes. Legumes are considered as useful and<br />
the cheapest source <strong>of</strong> nitrogen in pastures. On<br />
death and decay <strong>of</strong> the legume plant, their roots<br />
and root nodules break down in the soil and release<br />
their stored nitrogen, which then becomes<br />
available to the associated crops.<br />
Therefore, legume species like Afylosia sp.,<br />
Sesbania sp. and Stylo hamata were sown in the<br />
restoration sites. Further, species such as Sesbania<br />
produces high quality fodder, that can also be used<br />
as cattle feed.<br />
3.6 Soil Amendments in Bhirandiyara <strong>Restoration</strong><br />
Site<br />
The restoration site selected at Bhirandiyara was<br />
located in a highly saline track <strong>of</strong> <strong>Banni</strong>. In this site<br />
experimentation on salinity reduction and control<br />
22<br />
was undertaken to improve the grass diversity and<br />
productivity. This site was divided into four equal<br />
compartments, <strong>of</strong> which, compartment 1 is left under<br />
natural condition where no soil modifications<br />
were carried out. Compartment 2 was ploughed to a<br />
depth <strong>of</strong> 50 cm to improve the soil permeability,<br />
water infiltration and to break up-surface crust. In<br />
this compartment, organic manure was also added<br />
at the rate <strong>of</strong> 2 tons/ ha.<br />
To leach the salinity <strong>of</strong> the research site, a 5 m wide<br />
gentle slopes with a height <strong>of</strong> 30 cm and with 50 cm<br />
deep and 50 cm wide drainage channels were dug<br />
in the compartment 3. Similar activities, with<br />
changes in the width <strong>of</strong> the slopes to 3 m and height<br />
<strong>of</strong> the slopes to 50 cm were made in compartment 4<br />
to study the effects <strong>of</strong> increasing the slope height<br />
on the grass species diversity and productivity.<br />
The compartment 4 was further sub-divided into;<br />
half the slopes and the trench facing northwest<br />
direction and the other half facing east-west direction.<br />
The basic view <strong>of</strong> this amendment was to<br />
study the effects <strong>of</strong> wind borne salt deposition on<br />
the diversity and productivity <strong>of</strong> grass species<br />
growing on the slopes facing towards and against<br />
wind direction. It is hoped that this will help in generating<br />
an additional information on the deposition<br />
<strong>of</strong> salt particles through wind action and its impacts<br />
on the productivity <strong>of</strong> different grass species<br />
growing in the area.<br />
3.7 Soil Amendments in Dhordo <strong>Restoration</strong> Site<br />
The Dhordo restoration plot encompasses an area<br />
<strong>of</strong> 200 ha (width 1km x length 2km), located near<br />
village Dhordo. The whole area <strong>of</strong> the site was<br />
divided into 30m wide strips. Ploughing, adding <strong>of</strong><br />
farmyard manure and sowing <strong>of</strong> grass seeds were<br />
carried out in every alternative strips. Prosopis<br />
juliflora grown inside the fenced site was removed,<br />
except for few Prosopis juliflora, in which the side<br />
branches were removed with a view to change the<br />
architecture <strong>of</strong> the plant. There is a common view<br />
that the spreading cover <strong>of</strong> Prosopis juliflora<br />
reduces the underneath ground cover and that the<br />
changed architecture would help in supporting the<br />
underground vegetation. Further, the tree may also<br />
act as a windbreaker.