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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.

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