Full text: Resource and environmental monitoring (A)

  
  
JAPRS & SIS, Vol.34, Part 7, “Resource and Environmental Monitoring”, Hyderabad, India, 2002 
the wetland. This results in fertilization and resultant vegetative 
characteristic and floral biodiversity of the wetland. Salt waste 
area existent in the catchment is the main source of salts to Nal 
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
Table 5: Structural components, surrounding land use and their 
importance for avi-fauna 
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
Sarovar, which are deposited along with the runoff during Component Importance 
monsoon. Due to progressive evaporation from the wetland the Open Water Feeding habitat for waterfowls and resting 
wetland changes from fresh water to brackish to alkaline. value for ‘swimming’ waterfowl, boating 
for tourism and transportation, fishing, 
Table 4: Land use of Nal Sarovar Catchment irrigation and drinking, material for local 
Land use class | Area (ha) { % to total people, buffer against rain/storm water 
Catchment runoff and flooding of local rivers, abode 
Agricultural Land 60079.22 | 81.06 : of submerged vegetation, E 
Aquatic Food and cover for marsh inhabiting 
Salt waste 11727.87 15.82 ; > 
Vegetation waterfowl by emergent vegetation, and 
Mud flat 640.09 0.86 food for open water waterfowl by 
Grassland 359.82 0.76 submerged vegetation, thatching material 
Prosopis juliflora thickets 441.12 0.60 for local people and fodder for their 
Tank/pond 506.32 0.68 livestock. 
Settlement 163.54 0.22 Islet/plateau Resting and roosting value for waterfowls, 
SUB-TOTAL 74117.98 grazing of the livestock of local people. 
Wetland Edges of the islets also provide feeding 
Open Water 8189.09 47.56 opportunity to shorebirds. 
Ag. vegetation 514.94 2.99 Shoreline/ Habitat for waterfowls like shorebirds and 
Mud flat 6923.53 40.21 Basin cranes, grazing by livestock and 
Barren islets 383.00 2.22 recreational activity of tourists. 
Vegetated islets 74.32 0.43 Agricultural Feeding ground for migratory cranes, 
Salt waste 1032.33 5.99 land in the | agriculture and grazing activity by man. 
Agriculture . 103.69 0.60 environs 
SUB-TOTAL 17220.90 Wetlands in Secondary habitat for waterfowls and 
TOTAL 91338.88 environs Water needs of villages. 
Others No direct value to waterfowls but has 
Nal Sarovar catchment contains a significant area under 
ponds/tanks, which act as satellite wetlands and provide 
alternate habitats for waterfowl. À total of 37 such wetlands are 
present in its catchment. This is also one of the major reasons 
for rich faunal diversity of Nal Sarovar. 
5. CONCLUSIONS 
No quantitative study of biodiversity involving all its ecological 
facets has been carried out for the Nal Sarovar. According to a 
study carried out by Gujarat Ecological Education and Research 
Foundation (Anon., 1998), Nal Sarovar harbours 74 species of 
flowering plants, 48 species of algae and 226 species of birds. 
In addition to this, 13 species of mammals, 11 species of 
reptiles and large number of insects, zooplanktons etc. are also 
found in Nal Sarovar making it a very high biodiversity 
wetland. 
Habitat types and their temporal variations are the keystones for 
biodiversity conservation in wetlands. Present study has shown 
the utility of satellite data in mapping and monitoring of 
wetlands structural components/habitat types. These features 
determine the suitability of wetlands as habitats for waterfowl. 
As for example, Tatu (1995) has given details of structural 
components and their importance for Nal Sarovar (Table 5). 
As mentioned elsewhere, biodiversity of wetlands is a function 
of habitat types, its connectivity to the similar habitats in the 
vicinity and land use characteristics of the catchment. 
Catchment plays a major role in maintaining the characteristics 
of habitat types existing within a wetland ecosystem. The 
information on structural components and land use generated 
using remote sensing data in conjunction with on site data can 
be used for biodiversity conservation. A conceptual framework 
for wetland biodiversity conservation is given in Fig. 5. 
606 
  
  
  
  
ecological/socio-economic importance. 
Source: Tatu (1995) 
  
  
  
  
L- RS data | Collateral data | 
Wetland 
Structural components 
   
   
Wetland 
gradient 
    
  
   
  
N= =n 
  
  
  
  
    
Habitat types for 
Diversity prediction 
Habitat types 
  
  
  
  
2 -+2 
  
    
Species classification 
by habitat types using 
Species on faxa Biological database 
classifications 
Diversity o 
prediction 
BIODIVERSITY ASSESSMENT +] 
  
  
  
  
  
Fig.5: Conceptual framework for 
conservation 
wetland biodiversity 
The major threat to the Nal Sarovar wetland is the water 
availability which is rain dependent and highly erratic leading 
to drastic seasonal fluctuations in water level. The economy of 
the area is based on agriculture, animal husbandry, fishing and 
boating. All these activities generate low income, hence the 
people also resort to bird catching, poaching, fishing, boating, 
and grazing. These activities coupled with unregulated tourism 
are major factors leading to degradation of the fragile 
environment of this well-known bird sanctuary. Following steps 
are required to be taken to maintain the ecological character, 
functioning and biodiversity conservation of the Nal Sarovar:
	        
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