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Ecorestoration of Banni Grassland - Global Restoration Network

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Table 6: Grass and Herbaceous Species in and around Dhordo <strong>Restoration</strong> site<br />

<strong>Ecorestoration</strong> <strong>of</strong><br />

<strong>Banni</strong> <strong>Grassland</strong><br />

S. No Species<br />

Species Recorded in<br />

<strong>Restoration</strong> <strong>Restoration</strong> Site Out side Prosopis<br />

Site Unploughed Ploughed Area area<br />

1 Ahstida funiculata + + + + +<br />

2 Aeluropus logopoides + + + + +<br />

3 Cenchrus ciliaris + + + - -<br />

4 Cenchrus setigerus + + + + +<br />

5 Chlohs barbata + + + + +<br />

6 Cyperus rotundus + + + + +<br />

7 Cyperus haspan + + + - -<br />

8 Chrysopogan fulvus + + + - -<br />

9 Dactyloctenium aegyptium + + + + +<br />

10 Dichanthium annulatum + + + + +<br />

11 Digera muricata + + + + +<br />

12 Dinebra retr<strong>of</strong>lexa + + + + +<br />

13 Eragrostis tenella + + + + +<br />

14 Eragrostis sp. + + + + -<br />

15 Echinocloa sp. + + + + +<br />

16 Gandhiro* + + + + +<br />

17 Setaha pallide + + + - -<br />

18 Setaha sp. + + + + +<br />

19 Sporobolus helvolus + + + + +<br />

20 Sporobolus pallidus + + + - -<br />

21 Scirpus sp. + + - - -<br />

22 Tetrapogan tenellus + + + + +<br />

23 Tragus sp. + + + + +<br />

24 Themeda triandra + + - - -<br />

25 Cressa cretica + + + + +<br />

Total species 25 25 23 18 17<br />

% Occurrence 100.0 100.0 92.0 72.0 68.0<br />

* Unidentified species<br />

The list details the occurrence <strong>of</strong> species in the three sites. Some <strong>of</strong> the above mentioned species were<br />

not recorded in the sampling quadrates.<br />

seen only on vertical slopes while the occurrence<br />

<strong>of</strong> Chrysopogan fulvus and Setaria sp. were<br />

restricted only to the unploughed area (Table 7) <strong>of</strong><br />

the restoration site.<br />

5.3. SPECIES DISTRIBUTION PATTERN<br />

Plant distribution in an area is not homogenous. In<br />

nature, species that produce large number <strong>of</strong> wind<br />

dispersed seeds get scattered uniformly all over<br />

the area and on germination the plants grow<br />

throughout, while seeds <strong>of</strong> those species which do<br />

not have such dispersal mechanism, are generally<br />

shed near the plants or they are dispersed by animals<br />

or by other means. Such species are not scattered<br />

uniformly all over the area and their occur-<br />

rence is restricted to aggregation or in patches. The<br />

distribution pattern <strong>of</strong> species in an area can be<br />

obtained through percentage frequency estimation.<br />

Raunkaier (1934) classified five broad categories <strong>of</strong><br />

distribution based on the percentage frequency <strong>of</strong><br />

species. This classification was used to evaluate<br />

the distribution pattern <strong>of</strong> different grass species<br />

present in and around the study sites. Raunkaier’s<br />

frequency classes are as follows:<br />

Class A: Species with frequency from 1-20 per cent<br />

Class B: Species with frequency from 21- 40 per<br />

cent Class C: Species with frequency from 41- 60<br />

per cent Class D: Species with frequency from 61-<br />

80 per cent Class E: Species with frequency from<br />

81-100 per cent.<br />

29

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