IAPRS & SIS, Vol.34, Part 7, “Resource and Environmental Monitoring”, Hyderabad, India, 2002
acting as obstruction to the sediment movement. This had
resulted in erosion on the southern coast and deposition on the
northern coast. The IRS P4 OCM data are extremely useful to
study sediment dispersal and sediment transport studies due to
their 2-day repeat cycle. OCM data has been used for
computing advective velocity of surface currents (Prasad et al.
2002).
5. MARINE WATER QUALITY
Anthropogenic activities such as discharge of industrial and
municipal sewage, land use, tourism, maritime transport,
offshore oil exploration and production, dumping at sea
degrade the marine. environment. Turbidity and colour are
indicators of water quality. Chlorophyll indicates trophic status,
nutrient load and possibility of pollutants in coastal waters.
Suspended sediments affect navigation, fisheries, and aquatic
life, recreation potential of sea resorts. As the suspended
sediments carry absorbed chemicals and fronts are associated
with pollutants, the knowledge about their movement will help
in predicting waste effluent transportation path. Suspended
sediments are easily observed on the satellite imagery. Tides
play an important role in the movement of suspended sediments
and fronts (Nayak and Sahai, 1985). Successive images from
IRS P4 OCM have been used for understanding impact of tides
on sediments in tide- and wave-dominated regions. A distinct
front was observed separating the Gulf waters and the Arabian
Sea under different tidal conditions. This suggests that there is
very little mixing between these two waters. Hence the
poliutants discharged in the Gulf will circulate within the Gulf
and ultimately will settle in the Gulf itself.
Municipal sewage and industrial waste are major types of
pollution observed on the coast. Toxic chemicals, nutrients,
sediments and solid waste discharged in to coastal waters affect
coastal ecosystems. Such waste out-falls are difficult to detect
as near shore waters are turbid. Some of the effluents have
colour and can be detected. One such waste out-fall from
titanium factory near Thiruvananthapuram and sugar mill
discharge near the Kakinada Coast, West and east coast of India
were traced using high- resolution satellite data. Indian coastal
waters are relatively free from pollution except few pockets
around industrialised zones and large cities.
Oil spills from vessels and platforms are infrequent. In
such cases, oil rises to surface and spread across the
water body and thus amenable to remote detection. In
one such study, IRS P4 OCM data was used for
monitoring oil slick occurred in the Gulf of Kachchh.
However, 2-day repeat cycle of OCM data is not
adequate for monitoring slick in tide-dominated areas.
Satellite surveillance is possible if high-resolution remote-
sensing geo-synchronous satellite is available. Smaller spills
from vessels, maintenance of oil infrastructure is a major source
and is not detected on satellite images. Systematic observation
with high-resolution satellite data will be helpful to study their
effect on coastal habitats.
Incidences of harmful algal blooms have increased worldwide.
They may occur with cyclic regularity in certain regions where
certain optimum environmental conditions prevail in marine
waters. These planktons produce certain toxins, which
adversely affect fish and other organisms. The bloom usually
takes place rather suddenly and may spread with amazing
speed, changing colour of surface water into red, green or hay
colour. CZCS-derived chlorophyll map was used to study such
374
bloom in the Baltic Sea. IRS P4 OCM data have been used to
monitor Trichodesium bloom in the Arabian, Sea using OCM
data.
6. MARINE ENVIRONMENT AND CLIMATE CHANGE
The marine environment is sensitive and vulnerable to climate
change. It is necessary to determine present status of the
various systems and to predict future conditions. The high
degree of uncertainty in present information inhibits effective
management and limits the ability to make predictions and
assess environmental change. Systematic collection of data on
marine environment needed to apply integrated management
approaches and predict effect of global climate change. Global
climate change may compound pressures on coastal ecosystems
through warmer sea surface temperature, altered ocean
circulation patterns, changing storm frequency and rising sea
levels.
It was observed on IRS P4 images that productivity of the
coastal waters of the Orissa coast increased after the Orissa
cyclone Nayak et al. 2001). The frequency of cyclone has also
increased during last several years. It may be interesting to see
long-term impact on productivity in view of global warming.
Coral bleaching can occur due to increase in temperatures 1?-2?
C higher than average in the warm season. Coral bleaching
provides a direct indicator of the condition of coral reefs. In last
two decades, incidence of mass bleaching has been increasingly
observed (Goreau and Hayes, 1994, Goreau, et al. 1997).
NOAA SST data have been extensively used to study the
relationship between increase in SST and coral bleaching
(NOAA, 1998, ICRS, 1998). It is possible to predict coral :
bleaching by monitoring SST (Strong, 1998). The wide spread
coral bleaching observed during 1997-98 is an example of the
effect of elevated SST. This event of bleaching on the
Lakshadweep Islands, India was also recorded using IRS LISS
III data.
The sea level rise is highly variable both in terms of time and
space. Various estimates for the Indian coast vary from 0.5 to
2.2 mm per year. It is expected that the rise in sea level will
lead to increased erosion and habitat loss, increased salinity in
estuaries, alter tidal range, change sediment transport and
increase coastal flooding. Rising levels will also increase
impact of storm surges. The response of different ecosystems to
sea level rise has been evaluated based on their characteristics
for the Gujarat coast (Nayak, 1994). Small increase in sea level
has potential of causing significant changes to small islands and
low-lying coasts. It seems that conservation of mangrove areas
will be one of the Important steps to mitigate impact of the sea
level rise (Baba and Nayak, 2002).
7. COASTAL ZONE MANAGEMENT
The management of coastal zone requires data on varied
aspects as discussed earlier. Information exists in form of
thematic maps as well as non-spatial format. Thus it is difficult
to integrate these data conventionally. It is, therefore necessary
to develop a computer-based information system composed of
comprehensive and integrated set of data designed for
decision-making. In this remote-sensing-based management
plan, basic input about coastal areas is derived from remote
sensing data. Integration of this thematic data with other
secondary data would lead to identification of suitable sites and
initial zoning.
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