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IAPRS & SIS, Vol.34, Part 7, “Resource and Environmental Monitoring", Hyderabad, India, 2002
(Anonymous, 2001).Sonneratia apetala and Rhizophora
. lamarckii have become rare and nearing extinction
(Kannupandi and Kannan, 1998). Several studies provided
different estimates of degradation in different span of time but
actual cause for the degradation need to be ascertained.
Kannan et al (1998) estimated that 62.8% of 700 ha had
degraded during 1987 to 1994 with the aid of Survey of India
map and IRS IB LISS II data. Ramachandran and
Krishnamoorthy (1999) had attempted to demarcate mangrove
zonation in Pichavaram using TM and ERS-1 SAR and
reported that the SAR data was less useful in defining
mangrove areas due to differential back scattering by mangrove
canopy. Centre for Rural Education and Environmental
Development (CREED) had reported that the original 1,300 ha
cover of Pichavaram mangrove forest was reduced to 260 ha.
The degradation of Pichavaram mangrove was attributed to
human encroachment, charcoal production, fodder gathering
and cattle grazing (Anonymous, 2000).
Figure-1 Location of Pichavaram mangroves
M. S. Swaminathan Research Foundation (online) report
attributed physical factors such as seasonal closure of the
estuaries mouth and reduction in freshwater flow for the
degradation of mangrove wetland of Pichavaram rather than the
social causes. Based on water quality study, Purvaja and
Ramesh (2000) concluded that the fast degrading of mangroves
was due to natural and dominantly anthropogenic factors, like
damming of water in the upstream of the river Cauvery for
farming, leading to reduction in sediments supply needed for
mangrove vegetation. It was also reported that sea level rise of
approximately 1.5 mm/year leading to reduced tidal currents,
erosion of the substratum and increase in soil salinity might be
the causes for degradation of mangrove forests. Singh (2001)
had indicated that in Tamilnadu 47 sq. km of mangrove was
reduced to 21 sq. km during 1991-93 as per Forest Survey of
India estimates, of which Pichavaram forest forms a major
portion. During 1987 the Tamilnadu Forest Department
declared this zone as reserved forest. Since then no holistic
conservation and protection measure was taken up by
425
addressing all the possible issues for degradation barring efforts
taken up by Tamilnadu Forest Department, MSSR Foundation
and CAS in Marine Biology, Annamalai University, as per
available reports. Albeit, at this juncture, it is appropriate to
relook into the current status of Pichavaram mangroves, their
spatial extent, distribution and cause for the degradation.
Protection and conservation of Pichavaram mangroves and
restoration of the ecosystem require management solutions
purely based on the scientific analysis.
The zonation of the mangroves depends upon many factors like
morphology, hydrodynamics and other environmental
parameters in the intertidal region. Using remote sensing data it
was possible to identify different zones of degradation during
different time periods and address issues related to land use and
land cover changes due to developmental activities in the
coastal zone. Geographic Information System (GIS) is a
powerful technological tool for the integration of spatial data
like mangrove zonation, degradation, loss, land use and land
cover changes with non-spatial data like environmental
parameters and socio-economic data. Integration of mangrove
zonation, coastal morphology, hydrodynamics, environmental
conditions and socio-economic status of the region would
provide worthwhile solutions for the management of the
mangroves of Pichavaram.
Figure-2 Geography of Pichavaram mangrove environment
in IRS-1D, LISS data.
Classification of mangrove forest using Thematic Mapper data
is a proven technique (Sato and Kanetomi, 2000) but this study
attempted to classify different zones of the mangroves using
IRS-1D LISS III data. The Survey of India Topographic sheet
published in 1970 was used as a baseline information on spatial
distribution of the Pichavaram mangroves as the earliest
information available in reliable scale and accuracy. Using
23.5-metre resolution IRS-1D LISS four-band data of 1998, the
mangrove of Pichavaram was classified into three major zones
using unsupervised training sets. From the above classified
clusters, homogenous groups with more than 2 x 2 pixel