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Research Detail

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Md. Shahidul Islam*
Division of Applied Biosciences, Faculty of Fisheries, Graduate School of Agriculture, Kyoto University, Kyoto 606-8502, Japan

Md. Abdul Wahab
Department of Fisheries Management, Faculty of Fisheries, Bangladesh Agricultural University, Mymensingh 2202, Bangladesh

The mangrove forest of Bangladesh, the largest continuous mangrove bulk, is one of the most important features of the coastal area of the country. The existence of the mangrove has increased the values of other coastal and marine resources such as the coastal and marine fisheries by increasing productivity and supporting a wide biological diversity. The deltaic mangrove of Bangladesh is ecologically different from the other, mostly nondeltaic mangroves of the world and is unique also in its floral and faunal assemblage; therefore, a number of endangered plants and animals that are extinct from other parts of the world, are existing in Bangladesh mangrove. However, the mangrove has been under intensive pressure of exploitation for the last few decades which, in addition to direct clearance and conversion have placed the mangrove under extreme threat. Shrimp farming is the most destructive form of resource use the mangrove has been converted to, which contributed significantly to mangrove destruction with a corresponding loss of biological resources. Concerns have been raised among the ecologists, biologists, managers, and policymakers since the early 1990s; deliberate destruction of mangroves and unplanned development of coastal aquaculture particularly shrimp aquaculture have been put under extreme criticism and the sustainability has been questioned. The present status of the mangrove resources including mangrove fisheries and aquaculture and management practices have been reviewed in this paper; impacts of different forms of human interventions and resource use have also been discussed. It is suggested that the management options and the policy aspects should be critically reviewed and amended accordingly; beneficiaries and stakeholders at all levels of resource exploitation must take part and contribute to conservation and management. An immediate need for mangrove conservation has been identified.

  Mangrove, Sundarban, Shrimp farming, Fisheries, Bangladesh
  
  
  
  Socio-economic and Policy
  Status, Management

This paper reviews the present status of the mangrove resources and the main forms of coastal resource use with special emphasis on mangrove fisheries and aquaculture. The paper also discusses existing management practices and policy aspects, legislative and institutional issues as well as the impacts of various forms of resource use, and, finally, suggests options for better management and probable modes of rehabilitation of the exploited resources.

Mangrove flora The study of the floral diversity of the Sundarbans is limited to a group of commercially important species and few others. The forest supports a diverse plant genetic stock including timber species, wild relatives of cultivated plants and a number of endemic species. While most of the mangroves in other parts of the world are characterized by members of the Rhizophoraceae, Avicenniaceae, and Laganculariaceae, the mangroves of Bangladesh are dominated by the Streculiaceae and Euphorbiaceae. The mangroves of the Sundarbans are unique when compared to non-deltaic coastal mangrove forest; the reason for this difference is the large freshwater influence in the north-eastern part and the elevated level of the ground surface. Sunduri (Heritiera fomes) and Gewa (Excoecaria agallocha) are the dominant species, occurring in suitable localities along the coast. Unlike former times, Rhizophoraceae are now of minor importance. Inventory of the Sundarbans shows that there has been a change in favour of mixed Heritiera fomes and Excoecaria agallocha at the expense of pure Heritiera fomes forest. A further important change that the forest has undergone is a reduction in canopy density. In 1959, 78% of the forest had a canopy closure of 75% or more; now only 65% of the forest has canopy closure of 70% or more. Current inventory also shows that approximately 70% of Heritiera fomes stems are moderately or severely affected by topdying.

Mangrove fauna The mangrove forest provides a unique ecosystem and extensive habitats for a wide variety of faunal species. The Sundarbans is a very high quality wildlife conservation area of regional and international importance. Many authors have studied and given lists of the wildlife assemblages of the Sundarbans (Hendrichs, 1975; Mukherjee, 1975; Khan, 1982; Hussain et al., 1983; Sanyal, 1983, 1987; Khan, 1986, 1987; Seidensticker & Hai, 1983). The international importance of the Sundarbans as an essentially long-term wildlife habitat has also been documented (Gittins & Akonda, 1982; Seidensticker, 1986, 1987). Several studies (Seidenstiker & Hai, 1983; Blower, 1985a, b; Khan, 1986) reported that the mangroves of Bangladesh support at least 120 species of commercially important fishes, 290 species of birds, 42 species of mammals, 35 reptiles, and 8 species of amphibians. The mangroves also support a large number of species, which are now extinct elsewhere in the country. These include 2 amphibians, 14 reptiles, 25 birds, and 5 mammals.

Fish fauna The fishery resources are one of the primary concerns in the Sundarbans mangrove ecosystem. The fishery resources are characterized by a very high degree of endemism and diversity. The number of fish species available in the Sundarbans and their taxonomic status has been described among others by Rahman (1975, 1989) with varying degrees of accuracy. According to Hussain and Acharya (1994) the mangrove waters support 53 species of pelagic fish belonging to 27 families and 124 species under 49 families of demersal fish. However, this number is expected to be as high as 400 species using the mangrove swamps in various ways. Diadromous species such as Pangasius pangasius, Hilsa ilisha, Lates calcarifer are common in the low saline zone. The moderately saltwater zones are dominated by Hilsa ilisha; Pomadasys hasta, Polynemus spp., Coilia spp., Johnius spp. etc. The highly saline zones are likely to support species such as Harpodon nehereus; Trichiurus savala, Setipinna spp., Pampus spp., Sardinella spp., Salar spp. etc. Considerable seasonal changes also occur in the quality and quantity of fish fauna in the region. Over 120 species of fish are reported to be commonly caught by commercial fishermen in the Sundarbans. According to Mukherjee (1975) only brackish water species and marine forms are found in the Indian Sundarbans, freshwater species being totally absent. This may be assumed to apply also to the Bangladesh Sundarbans, except possibly in the eastern portion where there is freshwater in Baleswar River. Mention should also be made of mud-skippers or gobies which occur in large numbers and are a characteristic feature of mangrove swamps.

  Hydrobiologia (2005) 542:165–190
  DOI 10.1007/s10750-004-0756-y
Funding Source:
1.   Budget:  
  

The beneficial influence of mangrove forests is not limited to the immediate geographical area in which they grow. They exert balancing ecological influences that are felt far beyond their immediate boundaries. Although exploitation of mangroves for a long time and large-scale conversion of mangroves to aquaculture and other forms of resources have caused serious consequences, it is not impossible to rehabilitate the resources if proper attention is paid and effective management programs are formulated and practiced. A number of reports suggest that the mangrove Sundarbans of Bangladesh has been under a simple, easy-to-implement management regime that was installed more than a hundred years ago. The management regime has ensured sustainability and if the management practices are followed properly, this will ensure maintenance of the stands in stable condition for an indefinite period of time. Bangladesh is as rich in terms of its natural resources as it is poor in terms of its inadequate resource utilization and mobilization of its large human population for production and development purposes. Therefore, Bangladesh has to give a new look to its natural resources particularly to the coastal resources of how they can be used for the sustainable social and economic development of the country In old days, there was very poor knowledge on mangroves, and the forests were exploited without any scientific background, not considering the future implication of the exploitation. However, in recent days, knowledge of different aspects of the mangrove resources has increased greatly and mangrove resource conservation, management, and development have been paid considerable national and international attention. It has been fully realized and recognized in recent times that we are dependent to a great extent on the mangrove forests and they must be conserved for our own interests. Destruction of mangroves for coastal farming is now a global problem that has created considerable debate worldwide and needs proper attention and immediate action. The numbers of shrimp-producing and consuming nations are very few. These relatively few countries should provide a clear field of action on specific demands. The governments of these producing and consuming countries have a fundamental responsibility to enact legislation and enforce regulations to protect coastal and marine environments from destructive aquaculture practices. The multilateral development agencies such as the World Bank and the UN Food and Agriculture Organization, along with various national foreign aid programs, which have promoted and/or helped finance the destructive shrimp farming industry must review and amend their policies in this field, and redirect their support into rectifying the damage done.

  Journal
  


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