Full text: Resource and environmental monitoring (A)

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IAPRS & SIS, Vol.34, Part 7, “Resource and Environmental Monitoring", Hyderabad, India, 2002 
chemical properties and soil classification as per soil taxonomy 
(NRSA,1994b). The soil information along with other 
thematic information viz. land use / land cover, hydro- 
geomorphology etc., was used to assess the environmental 
impact of coal mining and in suggesting preventive measures 
for undertaking environmentally sustainable coal mining. 
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
Map Soil series Soil classification 
symbol (Dominant) 
2 Peddapaya L.S. Lithic Ustorthent 
8 Kondajutturu L.S. Lithic Ustorthents 
9 Ghani L.S. Ruptic Ustorthents 
10 Yerraguntla F.Typic Haplusterts 
11 Yerraguntla F.Typic Haplusterts 
14 Sugalimetta F.L. Typic Ustropepts 
19 Nandivargam C.L. Typic Ustifluvents 
20 Busanapalli | L.S. Lithic Ustorthents 
25 Rollapenta L.S. Typic Ustorthents 
35 Chintalacheruvu | L.S. Typic Ustropepts 
36 Kolimigundla F.Typic Haplusterts 
37 Midivemula F. Vertic Ustropepts 
38 Erusamala C.L. Typic Ustorthents 
39 Srisailam L.S.Typic Ustropepts 
Q Quarries 
  
  
  
  
  
Fig.2. Soil resource mapping of part of Kurnool District, 
Andhra Pradesh. 
À project entitled National Agricultural Technology Project 
has been taken up in the year 2000 with a view to study the 
natural resources including soil resources on watershed / micro 
watershed basis to generate action plans for improving the 
productivity in different production system. Implementation of 
action plan is in progress. 
The tribal areas of any country are unique in terms of terrain, 
climatic, socio-economic and natural resources. NRSA (1996c) 
had prepared soil maps along with other thematic maps like 
hydro-geomorphological, land use/ land cover, drainage etc, 
for tribal areas in parts Srikakulam, Vizianagaram, 
Visakhapatnam and East Godavri, districts of A.P at 1:50,000 
scale using IRS-IB satellite data. The soils of the study area 
were evaluated for land capability and specific soil problems of 
tribal areas were identified. The land degradational problems 
especially due to soil erosion by shifting cultivation were 
assessed and recommendations were given for development of 
land and water resources in the tribals areas. Similar study was 
also conducted in Gokavaram mandal in East Godavari district 
of Andhra Pradesh (NRSA, 1995). 
707 
2.7 Soil mapping at 1:25,000 and 1:12,500 scale 
From mid nineties onwards with the availability of 5.8m (PAN 
Sensor) and 23.5m spatial resolution data (LISS-III sensor) 
from IRS-1C/ID satellites, experiments have been carried out 
to prepare soil maps at 1:12,500 (NRSA, 1997c) and 1:25,000 
scales (NRSA,2002a) with PAN merged LISS-III data. In one 
of the studies at NRSA (1997c) with IRS-IC satellite data, PAN 
merged LISS-III data were utilised for mapping soils at 
1:12,500 scale in part of Kurnool district of Andhra Pradesh. 
The soils were mapped at individual soil series level. 
Subsequently, the soils of entire Dadra and Nagar Haveli Union 
Territory (UT) were mapped using IRS-ID satellite data along 
with other resources at 1:25,000 scale for Land use Board of 
Dadra and Nagar Haveli, U T. (NRSA,2002b). The soils were 
mapped at the level of association of soil series through visual 
interpretation of satellite data and ground truth.The soil 
information was used in the perspective land use planning for 
the U.T along with land use / land cover and hydro- 
geomorphology. Recently, under National Agricultural 
Technological Project (NATP) the soil maps at 1:12,500 scale 
are being prepared for different micro-watersheds under 
different crop production systems under different agro-climatic 
zones of the country. The information generated on various 
resources is being utilised for generation of action plans for 
improving the crop productivity in the micro-watersheds. 
3. LAND DEGRADTION MAPPING 
Lack of adequate information on soil resources led to 
improper land use planning which resulted in land 
degradational problems such as salinity / alkalinity and water 
logging in command areas, severe soil erosion in catchments, 
decrease in productivity of crops etc. According to National 
Commission on Agriculture (1976) 175 million hectares of 
land constituting 53.3% of the total geographical area of the 
country are subject to some kind of degradation. 
Mapping and monitoring of degraded lands with remotely 
sensed data proved to be comparatively easy because of 
distinct manifestation of various types of degraded lands like — 
salt affected soils, waterlogged areas, eroded areas, ravinous 
lands, shifting cultivation areas, mined areas, rock outcrops 
etc., on remotely sensed data. The repetitive nature of remote 
sensing satellites was exploited to monitor the effect of 
reclamation and conservation measures in the degraded lands. 
Survey of literature reveals that the satellite data were used to 
derive information on various aspects of degradaed lands — salt 
affected soils (Singh and Dwivedi, 1983,Rao et al.,1991, Rao et 
al,1995, NRSA, 1996b, 1997c, 2001, ) soil erosion 
(NRSA,1994), water logging (NRSA, 1996a, NRSA, 2000), 
ravinous lands (Venkataratnam and Ravisankar, 1992), waste 
lands (Annon, 2000), shifting cultivation ( Dwivedi and 
Ravisankar, 1992), impact assessment of soil conservation 
program in watershed (NRSA,1994), impact of aquaculture in 
coastal areas (Venkataratnam et al., 1997). 
At NRSA, the salt-affected soil maps for entire country were 
prepared at 1:250,000 scale using satellite data from Landsat 
TM/IRS sensors in association with central and state 
government organisations. Satellite data were also used on 
limited scale in the preparation of salt-affected soil maps of - 
Mainpuri and Unnao districts of UP, six south coastal districts 
of A.P (1:50,000 scale). The salt-affected soils and water 
 
	        
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