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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.,

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