ABSTRACTS / RESUMES - Comitato Glaciologico Italiano
ABSTRACTS / RESUMES - Comitato Glaciologico Italiano
ABSTRACTS / RESUMES - Comitato Glaciologico Italiano
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DAN BALTEANU<br />
Slope instability in the Vrancea seismogenic<br />
region (Romania)<br />
Institute of Geography of the Romanian Academy,<br />
12, Dimitrie Racovita, 70307 Bucaresti 20, Romania<br />
The most active subcrustal earthquake province in Europe<br />
(the Vrancea seismogenic region), lies in the South-eastern<br />
part of the Carpathian Mountains; it is characterised by an<br />
average of three seismic events in every century, including<br />
strong earthquakes of magnitude 7,2 ..7,4. The region is formed<br />
predominantly of folded and faulted Cretaceous and<br />
Palaeocene flysch and Neogene molasse and is characterised<br />
by an eccessive human pressure on the environment.<br />
Mass movements playa most significant role in the evolution<br />
of the relief and show a great diversity. The main controlling<br />
factor influencing the range of mass movements<br />
and their spatial and temporal distribution are the geological<br />
structure, seismic activity, climate and human activity.<br />
The papezr presents the distribution and variety of mass<br />
movements (landslides, mudflows and rockfalls) in connection<br />
with land use changes and different extreme<br />
events during the last century. The closely studied earthquake<br />
of Maich 4, 1977, magnitude 7,2 had marked effects<br />
on the relief of the epicentral area.<br />
The following phenomena were triggered by the March 4,<br />
1977 quake (magnitude M .,;- 7,2 on the Richter scale): 1.<br />
distinct movement of fault-line divided compartments; 2.<br />
emergence or reactivation of some mudvolcanoes; 3. deep<br />
slidings; 4. regression of steep slopes through fall and topple<br />
of rock fragments; 5. intensification of creep processes;<br />
6. formation of cracks in channel-beds and on slopes;<br />
7. suppression of clays and marls at the bottom of channelbeds;<br />
8. formation of sinking dolines on salt breccias; 9.<br />
collapse of gallery roof in some deserted mines; 10. liquefaction<br />
of loess deposits and sands; 11. underground water<br />
level changes; 12. emergence of highly mineralized<br />
springs.<br />
Our study will focus only those phenomena which brought<br />
changes in the morphology of slopes.<br />
SUNANDO BANDYOPADHYAY<br />
Coastal erosion in Sagar Island, Hugli Estuary, India:<br />
causes, consequences and human adjustments<br />
Department of Geography & Environment Management,<br />
Vidyasagar University, Medinipur 721102, WB, India<br />
The reclamation of Sagar island (21°37'-58'N; 88°02'<br />
11'E) from the Sundarban mangrove wetlands of the cyclone<br />
prone western Ganga-Brahmaputra delta was initiated<br />
in 1811. Mainly due to different government policies that<br />
64<br />
viewed the wetlands as waste lands and ignored the eroding<br />
nature of the coastal delta, the island has now become<br />
almost wholly settled with an agrarian population of<br />
184,942 (1997 estimate), growing by 40 per cent per decade.<br />
Coastal erosion, that steadily reduced the supratidal<br />
area of Sagar by a quarter within the last 143 years (from<br />
285 km 2 in 1851-55 to 213 km 2 in 1996) and at places triggered<br />
dune encroachment over farmland, forms the most<br />
important natural environmental hazard affecting this resident<br />
population. The conditions at Sagar are closely comparable<br />
with rest of the sea-board sections of the 5,360 km 2<br />
reclaimed Sundarban (Indian part) and the island can be<br />
used as a model for the region.<br />
Among other factors, the erosion of the island can primarily<br />
be linked to the reclamation process itself. It disturbed<br />
the morphological steady state of the resonant macrotidal<br />
Hugli estuary by reducing the intertidal area and increasing<br />
the mean depth of the channel. The abandoned and<br />
subsiding nature of the western delta as well as sediment<br />
sink in the Swatch of No Ground submarine canyon and<br />
in. the post-independence (1947) river valley projects also<br />
contributed to the problem. The erosional trend of Sagar<br />
is likely to continue in the future.<br />
Generally, most of the erosion takes place during the rainy<br />
monsoons (June-September). During this season, a destructive<br />
wave climate, increased occurrence.of tropical cyclones<br />
and a raised local sea level owing to increased fresh<br />
water input-all coincide. The severe cyclonic storms of<br />
Beaufort force 10 and above have a recurrence interval of<br />
3.28 years within 100 km of Sagar. The most destructive of<br />
these struck the island in 1833, 1864 and 1942, causing damages<br />
of the highest magnitude.<br />
The human adjustments to the erosion hazard include elementary<br />
technological control, acceptance, relocation, regulation<br />
and emergency measures-in that order. The erosion<br />
management schemes of Sagar are managed by seven<br />
government/semi-government agencies often with little<br />
coordination. These include 61 km of low ..tech marginal<br />
earthen embankments, built at US$ 7.2 per metre of length<br />
and requiring extensive unskilled maintenance; 14.5 km of<br />
comparatively more permanent brick-paved marginal embankments,<br />
built at US$ 62.9 per metre of length and re ..<br />
quiring skilled maintenance not always available locally;<br />
580 ha of mangrove plantations in 11 localities, three relocation<br />
projects involving about 250 families and 13 degraded<br />
storm refuges dating from the late 19th century. In a<br />
typical year, the calm late post-monsoon period (December-January)<br />
is the best time for repair or construction of<br />
the erosion prevention structures.<br />
For the present, achieving rational and coordinated use of<br />
the available resources with proper understanding of the<br />
natural feedback mechanisms would significantly ameliorate<br />
the efficiency of the existing management schemes. For<br />
the future, in view of the possible effects of the global<br />
greenhouse warming that might further increase the mean<br />
depth of the estuary and rate of coastal erosion, possibilities<br />
of gradual abandonment of the island for wetland<br />
restoration and relocating its population need to be considered.