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 />
s.<br />
No<br />
November and is followed by Cenchrus sp. (4.8 in<br />
September to 12.9 per cent in November) and<br />
Chloris barbata (5.9 in September to 9.8 per cent in<br />
November). These three species alone endowed<br />
nearly 32.7 per cent biomass in September, which<br />
increased to 58.8 per cent in November (Table 20).<br />
Though, Dichanthium annulatum recorded 37.5 per<br />
cent increase during the study period, its biomass<br />
contribution for the month <strong>of</strong> September was 8.2<br />
per cent which, decreased to 6.5 per cent in<br />
November. Further, the biomass production <strong>of</strong><br />
Dichanthium annulatum was found far lower than<br />
Sporobolus sp., which was 62.6 per cent lower in<br />
September and 82.1 per cent in November.<br />
At site B, except Eragrostis sp. and Aeluropus<br />
40<br />
Table 20: Biomass (kg/ha) Productivity <strong>of</strong> Different Species at Three sites <strong>of</strong> Dhordo<br />
Species<br />
1 CYPERUS SP. 250.0<br />
(15.2)<br />
Dhordo <strong>Restoration</strong> Site Degraded Area Prosopis juli flora Area<br />
Sep NOV %+/- SEP NOV %+/- SEP NOV %+/-<br />
188.9<br />
(6.5)<br />
2 C/I/ORIS BARBATA 97.8 (5.9) 283.0<br />
(9.8)<br />
3 SPOROBOLUS SP. 363.2<br />
(22.0)<br />
4 SETARIA SP. 225.0<br />
(13.7)<br />
1043.0<br />
(36.1)<br />
88.8<br />
(3.1)<br />
5 AELUROPUS SP. 22.1 (1.3) 192.6<br />
(6.7)<br />
6 ERAGROSTIS SP. 243.0<br />
(14.7)<br />
250.6<br />
(8.7)<br />
7 GANDHIRO 8.7 (0.5) 72.8<br />
(2.5)<br />
8 ECHINOCLOA SP. 54.5 (3.3) 174.0<br />
(6.0)<br />
9 CENCHRUS SP. 79.3 (4.8) 373.7<br />
(12.9)<br />
10 DACTYLOCTENIUM<br />
SP.<br />
-24.4 162.4<br />
(32.8)<br />
189.4 60.9<br />
(12.3)<br />
187.2 79.2<br />
(15.9)<br />
-60.5 76.2<br />
(15.4)<br />
771.1 88.8<br />
(17.9)<br />
8.1 1.6<br />
(0.3)<br />
27.0 -83.4 59.2<br />
(19.9)<br />
52.5<br />
(19.0)<br />
48.0<br />
(17.5)<br />
-13.8 32.6<br />
(10.9)<br />
62.0<br />
(34.8)<br />
40.67<br />
(22.8)<br />
4.7<br />
24.8<br />
-39.4 0.0 0.0 0.0<br />
0.0 -100.0 80.48<br />
(27.1)<br />
128.5<br />
(46.9)<br />
18.0<br />
(6.6)<br />
44.7 35.9<br />
(12.1)<br />
1025.0 36.4<br />
(12.2)<br />
736.8 22.8 0 0.0 ~ 18.4<br />
(6.2)<br />
12.0<br />
(6.7)<br />
24.7<br />
(13.9)<br />
38.7<br />
(21.7)<br />
-85.1<br />
-31.2<br />
6.3<br />
0.0 -100.0<br />
219.3 0.0 0.0 0.0 0.0 0.0 0.0<br />
371.2 0.0 0.0 0.0 4.6 0 0.0 -100.0<br />
135.7 (8.2) 2.0 0 -88.5 0.0 0.0 0.0 29.6 0 0.0 -100.0<br />
11 TETRAPOGAN SP. 32.5 36.9 13.5 0.0 0.0 0.0 0.0 0.0 0.0<br />
12 DICHANTHIUM SP. 135.9 (8.2) 186.8<br />
(6.5)<br />
37.5 3.4<br />
(0.7)<br />
0.0 ~ 0.0 0.0 0.0<br />
TOTAL BIOMASS 287.7 217.2 75.6 2.7 11.4.0 -44.7 0.0 17 -40.1<br />
AVERAGE 70.6 83.8 62.5 90.0 62.3 65.1<br />
percentage are given in parenthesis<br />
logopoides all other species showed a decrease,<br />
while at site C except Chloris barbata, Cyperus<br />
rotundas and Eragrostis sp. all other species<br />
showed increasing trend. At site B, the Aeluropus<br />
logopoides showed an increase <strong>of</strong> 44.7 per cent<br />
during the study period, and contributed 17.8 per<br />
cent <strong>of</strong> biomass in September, which further<br />
increased to 46.9 per cent in November. The<br />
biomass <strong>of</strong> highly palatable species such as<br />
Dichanthium annulatum, Gandhiro was totally<br />
grazed out and Sporobolus sp. was much reduced<br />
at site B and C.<br />
The comparison <strong>of</strong> biomass <strong>of</strong> different species<br />
between September and November showed that<br />
the productivity <strong>of</strong> species such as Cenchrus sp.,