Ministry of Regional Municipalities; Environment
National Biodiversity Strategy and Action Plan Technical Report
no. 369, 2001.
Abstract | BibTeX | Tags: conservation, ecosystem, education, endangered, Fisheries, guiding, habitat, management, marine, objectives, Oman, population, productivity, protected areas, status
@techreport{,
title = {National Biodiversity Strategy and Action Plan},
author = {Ministry of Regional Municipalities and Environment},
year = {2001},
date = {2001-01-01},
volume = {86/2001},
number = {369},
pages = {1-56},
abstract = {Executive Summary Implementing the Convention on Biological Diversity Biodiversity supports human societies ecologically, economically, culturally and spiritually. Despite its importance, ecosystems are degrading and the species and genetic diversity reducing at an alarming rate due to the impact of growing human population and increasing resource consumption. The global decline of biodiversity is now recognized as one of the most serious environmental issues facing humanity. This inspired the global community to negotiate the United Nations Convention on Biological Diversity. Delegation from Oman actively participated in these negotiations and the Government of Oman signed the Convention in June 1992 and ratified it in 1994. The three objectives of the Biodiversity Convention are: -the conservation of biodiversity; -the sustainable use of biological resources; and -the fair and equitable sharing of benefits resulting from the use of genetic resources. These objectives form the three pillars of sustainable development, ecological integrity, economic sustainability and social equity thus illustrating the nature and scope of the Convention. As a global instrument, it sets the stage for each nation to assess the adequacy of current efforts to conserve biodiversity and sustainable use of biological resources and to determine how inadequacies will be rectified. One of the key obligations of the signatory parties to the Convention is to prepare a national biodiversity strategy and action plan. Thus, the National Biodiversity Strategy and Action Plan is a response to this obligation. It has been developed to guide the implementation of the Biodiversity Convention in Oman. All strategic directions contained in the Strategy are relevant from a national perspective. The National Biodiversity Strategy and Action Plan recognizes existing constitutional and legislative responsibilities for biodiversity in Oman. It also emphasizes the importance of intergovernmental co-operation to create the policy, management and research to advance ecological management. National and regional governments, sectoral agencies, and other stakeholders including the members of the public, will pursue the implementation of the Strategy as guided by their administrative and fiscal capabilities. Elements of the National Strategy and Action Plan Vision: The National Strategy and Action Plan presents a vision for Oman of: A society that is conscious of the role and issues related to biological diversity, convinced of its responsibilities toward future generations and determined to sustainably use natural resources in harmony with all other living things in accordance with the teachings of Islam. In support of this vision, the Strategy presents a series of guiding principles that provide a foundation for implementation. The Strategy provides a framework for action that will enhance our ability to ensure productivity, diversity and integrity of our natural ecosystems and, as a result, our ability as a nation to develop sustainably. It promotes the conservation of biodiversity and the sustainable use of biological resources, and describes how we will complement international efforts to implement the Convention. Mission: "To conserve the biological diversity of the Sultanate and its terrestrial and marine environment, in accordance with the articles of the Convention on Biological Diversity, for the benefit of the present and future generations of Omanis and for mankind as a whole, with respect to the guiding principles of Islam. " Main strategic goals: -Safeguard habitats and productive renewable resources for rational and sustainable exploitation .-Conserve habitat, plant and animal diversity especially of those uncommon and also of special interest; -Provide a high quality natural environment for recreational and tourist activities; - Improve the understanding of ecosystems and increase resource management capability; - Advocate the need to conserve biodiversity and use biological resources in a sustainable manner; - Develop legislation that insures the conservation of biodiversity and the sustainable use of biological resources; - Develop incentives that will promote, biodiversity conservation and provide employment for local people; - Equitably share the benefits of sustainable resources including genetic resources at local and regional levels. - Promote regional and international collaboration on biodiversity conservation and sustainability of natural resources. Proposed mechanisms for implementation: - Creation of a permanent interministerial biodiversity steering Committee and National Biodiversity office which will be responsible for : 1) the filing of an annual national report on policies, activities and plans aimed at implementing the Strategy; 2) co-ordinating the implementation of national and international elements of the Strategy; 3) recommend measures to permit and encourage non-government participation in the implementation of the Strategy; 4) Regular reporting on the status of biodiversity; and, 5) revision of the strategy after an initial implementation phase of five years. The National Strategy and Action Plan proposes a series of priority actions that are classified according to the following themes involving most sectors of society: .Conservation of Natural Resources (Protected areas, Endangered species, conservation) .Terrestrial and Freshwater Fauna . Marine Life and Fisheries .Terrestrial and Aquatic Flora .Agriculture Resources.Energy Resources .Mineral Resources .Industry, Technology and Services (Biotechnology and Biosafety, Tourism) .Urban Environment .Water Resources .Environmental Emergencies .Participation of the Public, Non-Governmental Organisations and Private Sector .Societal Values (Public awareness, education and training; Environmental impact assessments; Institutional and legal framework) .Quality of Life .Spiritual Values },
keywords = {conservation, ecosystem, education, endangered, Fisheries, guiding, habitat, management, marine, objectives, Oman, population, productivity, protected areas, status},
pubstate = {published},
tppubtype = {techreport}
}
Executive Summary Implementing the Convention on Biological Diversity Biodiversity supports human societies ecologically, economically, culturally and spiritually. Despite its importance, ecosystems are degrading and the species and genetic diversity reducing at an alarming rate due to the impact of growing human population and increasing resource consumption. The global decline of biodiversity is now recognized as one of the most serious environmental issues facing humanity. This inspired the global community to negotiate the United Nations Convention on Biological Diversity. Delegation from Oman actively participated in these negotiations and the Government of Oman signed the Convention in June 1992 and ratified it in 1994. The three objectives of the Biodiversity Convention are: -the conservation of biodiversity; -the sustainable use of biological resources; and -the fair and equitable sharing of benefits resulting from the use of genetic resources. These objectives form the three pillars of sustainable development, ecological integrity, economic sustainability and social equity thus illustrating the nature and scope of the Convention. As a global instrument, it sets the stage for each nation to assess the adequacy of current efforts to conserve biodiversity and sustainable use of biological resources and to determine how inadequacies will be rectified. One of the key obligations of the signatory parties to the Convention is to prepare a national biodiversity strategy and action plan. Thus, the National Biodiversity Strategy and Action Plan is a response to this obligation. It has been developed to guide the implementation of the Biodiversity Convention in Oman. All strategic directions contained in the Strategy are relevant from a national perspective. The National Biodiversity Strategy and Action Plan recognizes existing constitutional and legislative responsibilities for biodiversity in Oman. It also emphasizes the importance of intergovernmental co-operation to create the policy, management and research to advance ecological management. National and regional governments, sectoral agencies, and other stakeholders including the members of the public, will pursue the implementation of the Strategy as guided by their administrative and fiscal capabilities. Elements of the National Strategy and Action Plan Vision: The National Strategy and Action Plan presents a vision for Oman of: A society that is conscious of the role and issues related to biological diversity, convinced of its responsibilities toward future generations and determined to sustainably use natural resources in harmony with all other living things in accordance with the teachings of Islam. In support of this vision, the Strategy presents a series of guiding principles that provide a foundation for implementation. The Strategy provides a framework for action that will enhance our ability to ensure productivity, diversity and integrity of our natural ecosystems and, as a result, our ability as a nation to develop sustainably. It promotes the conservation of biodiversity and the sustainable use of biological resources, and describes how we will complement international efforts to implement the Convention. Mission: "To conserve the biological diversity of the Sultanate and its terrestrial and marine environment, in accordance with the articles of the Convention on Biological Diversity, for the benefit of the present and future generations of Omanis and for mankind as a whole, with respect to the guiding principles of Islam. " Main strategic goals: -Safeguard habitats and productive renewable resources for rational and sustainable exploitation .-Conserve habitat, plant and animal diversity especially of those uncommon and also of special interest; -Provide a high quality natural environment for recreational and tourist activities; - Improve the understanding of ecosystems and increase resource management capability; - Advocate the need to conserve biodiversity and use biological resources in a sustainable manner; - Develop legislation that insures the conservation of biodiversity and the sustainable use of biological resources; - Develop incentives that will promote, biodiversity conservation and provide employment for local people; - Equitably share the benefits of sustainable resources including genetic resources at local and regional levels. - Promote regional and international collaboration on biodiversity conservation and sustainability of natural resources. Proposed mechanisms for implementation: - Creation of a permanent interministerial biodiversity steering Committee and National Biodiversity office which will be responsible for : 1) the filing of an annual national report on policies, activities and plans aimed at implementing the Strategy; 2) co-ordinating the implementation of national and international elements of the Strategy; 3) recommend measures to permit and encourage non-government participation in the implementation of the Strategy; 4) Regular reporting on the status of biodiversity; and, 5) revision of the strategy after an initial implementation phase of five years. The National Strategy and Action Plan proposes a series of priority actions that are classified according to the following themes involving most sectors of society: .Conservation of Natural Resources (Protected areas, Endangered species, conservation) .Terrestrial and Freshwater Fauna . Marine Life and Fisheries .Terrestrial and Aquatic Flora .Agriculture Resources.Energy Resources .Mineral Resources .Industry, Technology and Services (Biotechnology and Biosafety, Tourism) .Urban Environment .Water Resources .Environmental Emergencies .Participation of the Public, Non-Governmental Organisations and Private Sector .Societal Values (Public awareness, education and training; Environmental impact assessments; Institutional and legal framework) .Quality of Life .Spiritual Values
De Sylva,D.
The need for monitoring of artificial reef structures; Guidelines for an artificial reef monitoring programme for Oman Journal Article
In: Marine Policy, no. 358, pp. 1 -27, 2000.
Abstract | BibTeX | Tags: artificial reefs, coastal management, Fisheries, marine, monitoring, objectives, Oman, pollution, worldwide
@article{,
title = {The need for monitoring of artificial reef structures; Guidelines for an artificial reef monitoring programme for Oman },
author = {De Sylva,D.},
year = {2000},
date = {2000-01-01},
journal = {Marine Policy},
number = {358},
pages = {1 -27},
abstract = {Globally, 36% of all reefs were classified as threatened by overexploitation, 30% by coastal development, 22% by inland pollution and erosion, and 12% by marine pollution. These human activities coupled with natural disasters have led to reductions in the natural reef systems and marine resources world-wide. Artificial reefs are being deployed in a hope to rehabilitate declining reef systems and enhance fisheries, among other things. In order to assess how successful these structures are in fulfilling their objectives monitoring needs to be carried out. This paper will provide suitable guidelines for a monitoring program to be used on artificial reefs.},
keywords = {artificial reefs, coastal management, Fisheries, marine, monitoring, objectives, Oman, pollution, worldwide},
pubstate = {published},
tppubtype = {article}
}
Globally, 36% of all reefs were classified as threatened by overexploitation, 30% by coastal development, 22% by inland pollution and erosion, and 12% by marine pollution. These human activities coupled with natural disasters have led to reductions in the natural reef systems and marine resources world-wide. Artificial reefs are being deployed in a hope to rehabilitate declining reef systems and enhance fisheries, among other things. In order to assess how successful these structures are in fulfilling their objectives monitoring needs to be carried out. This paper will provide suitable guidelines for a monitoring program to be used on artificial reefs.
Garrison,D.L.,Gowing,M.M.,Hughes,M.P.,Campbell,L.,Caron,D.A.,Dennett,M.R.,Shalapyonok,A.,Olson,R.J.,Landry,M.R.,Brown,S.L.,Liu,H.-B.,Azam,F.,Steward,G.F.,Ducklow,H.W.,Smith,D.C.
Microbial food web structure in the Arabian Sea: a US JGOFS study Journal Article
In: Deep-Sea Research Part II, vol. 47 , no. 98, pp. 1387-1422, 2000.
Abstract | BibTeX | Tags: Arabian Sea, dominance, objectives, salinity, temperature, Upwelling
@article{,
title = {Microbial food web structure in the Arabian Sea: a US JGOFS study},
author = {Garrison,D.L.,Gowing,M.M.,Hughes,M.P.,Campbell,L.,Caron,D.A.,Dennett,M.R.,Shalapyonok,A.,Olson,R.J.,Landry,M.R.,Brown,S.L.,Liu,H.-B.,Azam,F.,Steward,G.F.,Ducklow,H.W.,Smith,D.C.},
year = {2000},
date = {2000-01-01},
journal = {Deep-Sea Research Part II},
volume = {47 },
number = {98},
pages = {1387-1422},
abstract = {One of the main objectives of the Joint Global Ocean Flux Studies (JGOFS) program is to develop an understanding of the factors controlling organic carbon production in the ocean and the time-varying vertical flux of carbon from surface waters (US JGOFS (1990) US JGOFS Planning Report Number 11; Sarmiento and Armstrong (1997) US JGOFS Synthesis and Modeling Project Implementation Plan). A considerable amount of evidence suggests that carbon cycling and the potential for exporting carbon from ocean systems is a function of food web structure. As part of the US JGOFS Arabian Sea Studies, the biomass of planktonic organisms, ranging from heterotrophic bacteria through microplankton-sized organisms, was estimated using a variety of methods including flow cytometry and microscopy. This is a first attempt to combine biomass data from a number of sources, evaluate the structure of the food web, examine changes in food web structure in relation to seasonal or spatial features of the study area, and look for indications of how changing structure affects carbon-cycling processes. Biomass in the upper 100 m of the water column ranged from approximately 1.5 to >5.2 gC m-2. Heterotrophic bacteria (Hbac) made up from 16 and 44% of the biomass; autotrophs comprised 43-64%; and the remainder was made up of nano- and microheterotrophs. Autotrophs and nano- and microheterotrophs showed a general pattern of higher values at coastal stations, with the lowest values offshore. Heterotrophic bacteria (Hbac) showed no significant spatial variations. The Spring Intermonsoon and early NE Monsoon were dominated by autotrophic picoplankton, Prochlorococcus and Synechococcus. The late NE Monsoon and late SW Monsoon periods showed an increase in the larger size fractions of the primary producers. At several stations during the SW Monsoon, autotrophic microplankton, primarily diatoms and Phaeocystis colonies, predominated. Increases in the size of autotrophs were also reflected in increasing sizes of nano- and microheterorophs. The biomass estimates based on cytometry and microscopy are consistent with measurement of pigments, POC and PON. Changes in community structure were assessed using the percent similarity index (PSI) in conjunction with multidimensional scaling (MDS) or single-linkage clustering analysis to show how assemblages differed among cruises and stations. Station clustering reflected environmental heterogeneity, and many of the conspicuous changes could be associated with changes in temperature, salinity and nutrient concentrations. Despite inherent problems in combining data from a variety of sources, the present community biomass estimates were well constrained by bulk measurements such as Chl a, POC and PON, and by comparisons with other quantitative and qualitative studies. The most striking correlation between food web structure and carbon cycling was the dominance of large phytoplankton, primarily diatoms, and the seasonal maxima of mass flux during the SW Monsoon. High nutrient conditions associated with upwelling during the SW Monsoon would explain the predominance of diatoms during this season. The sinking of large, ungrazed diatom cells is one possible explanation for the flux observations, but may not be consistent with the observation of concurrent increases in larger microzooplankton consumers (heterotrophic dinoflagellates and ciliates) and mesozooplankton during this season. Food-web structure during the early NE Monsoon and Intermonsoons suggests carbon cycling by the microbial community predominated.},
keywords = {Arabian Sea, dominance, objectives, salinity, temperature, Upwelling},
pubstate = {published},
tppubtype = {article}
}
One of the main objectives of the Joint Global Ocean Flux Studies (JGOFS) program is to develop an understanding of the factors controlling organic carbon production in the ocean and the time-varying vertical flux of carbon from surface waters (US JGOFS (1990) US JGOFS Planning Report Number 11; Sarmiento and Armstrong (1997) US JGOFS Synthesis and Modeling Project Implementation Plan). A considerable amount of evidence suggests that carbon cycling and the potential for exporting carbon from ocean systems is a function of food web structure. As part of the US JGOFS Arabian Sea Studies, the biomass of planktonic organisms, ranging from heterotrophic bacteria through microplankton-sized organisms, was estimated using a variety of methods including flow cytometry and microscopy. This is a first attempt to combine biomass data from a number of sources, evaluate the structure of the food web, examine changes in food web structure in relation to seasonal or spatial features of the study area, and look for indications of how changing structure affects carbon-cycling processes. Biomass in the upper 100 m of the water column ranged from approximately 1.5 to >5.2 gC m-2. Heterotrophic bacteria (Hbac) made up from 16 and 44% of the biomass; autotrophs comprised 43-64%; and the remainder was made up of nano- and microheterotrophs. Autotrophs and nano- and microheterotrophs showed a general pattern of higher values at coastal stations, with the lowest values offshore. Heterotrophic bacteria (Hbac) showed no significant spatial variations. The Spring Intermonsoon and early NE Monsoon were dominated by autotrophic picoplankton, Prochlorococcus and Synechococcus. The late NE Monsoon and late SW Monsoon periods showed an increase in the larger size fractions of the primary producers. At several stations during the SW Monsoon, autotrophic microplankton, primarily diatoms and Phaeocystis colonies, predominated. Increases in the size of autotrophs were also reflected in increasing sizes of nano- and microheterorophs. The biomass estimates based on cytometry and microscopy are consistent with measurement of pigments, POC and PON. Changes in community structure were assessed using the percent similarity index (PSI) in conjunction with multidimensional scaling (MDS) or single-linkage clustering analysis to show how assemblages differed among cruises and stations. Station clustering reflected environmental heterogeneity, and many of the conspicuous changes could be associated with changes in temperature, salinity and nutrient concentrations. Despite inherent problems in combining data from a variety of sources, the present community biomass estimates were well constrained by bulk measurements such as Chl a, POC and PON, and by comparisons with other quantitative and qualitative studies. The most striking correlation between food web structure and carbon cycling was the dominance of large phytoplankton, primarily diatoms, and the seasonal maxima of mass flux during the SW Monsoon. High nutrient conditions associated with upwelling during the SW Monsoon would explain the predominance of diatoms during this season. The sinking of large, ungrazed diatom cells is one possible explanation for the flux observations, but may not be consistent with the observation of concurrent increases in larger microzooplankton consumers (heterotrophic dinoflagellates and ciliates) and mesozooplankton during this season. Food-web structure during the early NE Monsoon and Intermonsoons suggests carbon cycling by the microbial community predominated.
Clark,J.E.
Proposals for a System of Nature Conservation Areas Technical Report
no. 348, 1986.
Abstract | BibTeX | Tags: cetacean, conservation, endangered, habitat, Humpback Whale, management, marine, objectives, Oman, population, populations, survey, whale
@techreport{,
title = {Proposals for a System of Nature Conservation Areas},
author = {Clark,J.E.},
year = {1986},
date = {1986-01-01},
number = {348},
pages = {1-477},
publisher = {IUCN},
abstract = {This report describes the outcome of a nature conservation project set up by the Government of the Sultanate of Oman and the International Union for the Conservation of Nature and Natural Resources (IUCN). Oman is a state member of IUCN. The project was operational for almost 20 months, starting in October 1984. An IUCN consultant Project Leader and an Omani Assistant Project Leader were employed full time. Five other IUCN specialists were employed on short term consultancies. The project's goal was to prepare in-depth plans for a system of nature conservation areas (NCAs) in Oman. The resultant nature conservation programme would form part of Oman's total land use strategy. The plans were to include prescriptions for policy and law; the design of a NCA system; and proposals for the structure and operation of a Directorate General of Wildlife and Nature Conservation. This new Government entity is expected to be set up in the Ministry of the Environment and Water Resources . The specific requirements for the proposed NCA system were threefold. Firstly, it should be representative of Oman's varied wild habitats, terrestrial and marine: we identified, described and mapped 43 different Land Classes and 12 Marine Habitats. Secondly, it should conserve populations of all threatened and endemic wildlife found in Oman, and other species judged to be of special interest: we identified 94 plant and 100 animal taxa that fell within this grouping. Thirdly, it should protect selected sites and areas, chosen because they had interesting biotic or abiotic features. We identified and described 89 such sites. The sites comprised desert pools and seepages, coastal lagoons, tidal inlets, marine sites, botanical sites, caves, geological and geomorphological sites and landscapes. The resultant system that we designed consists of 91 NCAs, dispersed widely throughout Oman, and covering a total area of 119,798 sq. km. We proposed that there should be three different categories of NCA: national nature reserve (NNR), 59 areas; national scenic reserve (NSR), 20 areas; and national resource reserve (NRR), 12 areas. NNRs are the most strictly managed category: permanent human settlement is not permitted. NSRs may contain human settlement but the laws provide mechanisms for controlling human activities in conformity with nature conservation objectives. NRR is a temporary category of NCA, given to areas that are clearly of interest but about which insufficient is known to justify delineating NCA boundaries. NRRs are identified as priority areas for further studies that may lead to their becoming NNRs or NSRs. We also provided for the protection of selected wildlife outside the NCA system. We recommended two categories of protected wildlife: those that should be granted full protection, and those that be partially protected to the extent that controlled, licensed taking could be permitted. (The only cetacean species mentioned in this list is the humpback whale, which is tentatively classified as endangered. This is probably due to the lack of information about any other species at that time. Marine sites proposed for protection were selected "ont he basis of their having interesting sublittoral features". Selection was on the basis of biological or scenic characteristics. The authors acknowledge that the survey was limited in its study of marine sites, but believe that their proposals include so many long stretches of coastline that important habitats will be included. Marine areas proposed for first priority in active management (NNRs) include Jazirat Umm al Fayyarin (Musandam), Ras Suwadi, Daymaniyat Islands, Qurm/Fahal, Bandar Jissah, Ras al Hadd, Ras al Junays, Barr al Hikmann, Hasikiyah, Qibliyah, Marbat, Khawr Rawri and Khawr Salalah. Sawda and Hallaniya are propsed as NSR's.},
keywords = {cetacean, conservation, endangered, habitat, Humpback Whale, management, marine, objectives, Oman, population, populations, survey, whale},
pubstate = {published},
tppubtype = {techreport}
}
This report describes the outcome of a nature conservation project set up by the Government of the Sultanate of Oman and the International Union for the Conservation of Nature and Natural Resources (IUCN). Oman is a state member of IUCN. The project was operational for almost 20 months, starting in October 1984. An IUCN consultant Project Leader and an Omani Assistant Project Leader were employed full time. Five other IUCN specialists were employed on short term consultancies. The project's goal was to prepare in-depth plans for a system of nature conservation areas (NCAs) in Oman. The resultant nature conservation programme would form part of Oman's total land use strategy. The plans were to include prescriptions for policy and law; the design of a NCA system; and proposals for the structure and operation of a Directorate General of Wildlife and Nature Conservation. This new Government entity is expected to be set up in the Ministry of the Environment and Water Resources . The specific requirements for the proposed NCA system were threefold. Firstly, it should be representative of Oman's varied wild habitats, terrestrial and marine: we identified, described and mapped 43 different Land Classes and 12 Marine Habitats. Secondly, it should conserve populations of all threatened and endemic wildlife found in Oman, and other species judged to be of special interest: we identified 94 plant and 100 animal taxa that fell within this grouping. Thirdly, it should protect selected sites and areas, chosen because they had interesting biotic or abiotic features. We identified and described 89 such sites. The sites comprised desert pools and seepages, coastal lagoons, tidal inlets, marine sites, botanical sites, caves, geological and geomorphological sites and landscapes. The resultant system that we designed consists of 91 NCAs, dispersed widely throughout Oman, and covering a total area of 119,798 sq. km. We proposed that there should be three different categories of NCA: national nature reserve (NNR), 59 areas; national scenic reserve (NSR), 20 areas; and national resource reserve (NRR), 12 areas. NNRs are the most strictly managed category: permanent human settlement is not permitted. NSRs may contain human settlement but the laws provide mechanisms for controlling human activities in conformity with nature conservation objectives. NRR is a temporary category of NCA, given to areas that are clearly of interest but about which insufficient is known to justify delineating NCA boundaries. NRRs are identified as priority areas for further studies that may lead to their becoming NNRs or NSRs. We also provided for the protection of selected wildlife outside the NCA system. We recommended two categories of protected wildlife: those that should be granted full protection, and those that be partially protected to the extent that controlled, licensed taking could be permitted. (The only cetacean species mentioned in this list is the humpback whale, which is tentatively classified as endangered. This is probably due to the lack of information about any other species at that time. Marine sites proposed for protection were selected "ont he basis of their having interesting sublittoral features". Selection was on the basis of biological or scenic characteristics. The authors acknowledge that the survey was limited in its study of marine sites, but believe that their proposals include so many long stretches of coastline that important habitats will be included. Marine areas proposed for first priority in active management (NNRs) include Jazirat Umm al Fayyarin (Musandam), Ras Suwadi, Daymaniyat Islands, Qurm/Fahal, Bandar Jissah, Ras al Hadd, Ras al Junays, Barr al Hikmann, Hasikiyah, Qibliyah, Marbat, Khawr Rawri and Khawr Salalah. Sawda and Hallaniya are propsed as NSR's.
Alling,G.,Gordon,J.,Rotton,N.,Whitehead,H.
Indian Ocean Sperm Whale study, 1981 - 1982 interim report Technical Report
no. 281, 1982.
Abstract | BibTeX | Tags: behaviour, dolphin, dolphins, Eubalaena glacialis, Fisheries, Humpback Whale, humpback whales, Indian Ocean, marine, marine mammal, megaptera novaeangliae, objectives, Oman, physeter, population, populations, sanctuaries, sperm whale, sperm whales, survey, whale, whales
@techreport{,
title = {Indian Ocean Sperm Whale study, 1981 - 1982 interim report},
author = {Alling,G.,Gordon,J.,Rotton,N.,Whitehead,H.},
year = {1982},
date = {1982-01-01},
number = {281},
pages = {1-43},
publisher = {WWF},
abstract = {The establishment of the Indian Ocean Whale Sanctuary in 1979 gave whale science an opportunity and a challenge: the opportunity to study protected whale; and the challenge to show that whale populations can be monitored purely through studies of living animals. The sperm whale (Physeter catodon), is commercially the most important, and the most numerous, large whale. It may be a significant link in the food web on account of returning nutrients from the deep ocean to the surface through its faeces. Analysis of the composition of sperm whale catches suggests that the sperm whale possesses a unique and interesting social system (Best 1979), a thorough knowledge of which is essential if these exceptional animals are to be properly protected.It was thus appropriate to carry out a study of the behaviour of the sperm whales in the Indian Ocean, principally using the methods developed on living right, grey and humpback whales, and the money raised by WWF-Netherlands. In order to obtain significant results it was thought necessary to have three field seasons of several months each.As very little was known of the whales of the Indian Ocean the first season consisted of a survey of those parts of the NW Indian Ocean which might have been suitable for studying sperm whales. During the survey methods of studying living sperm whales were to be developed, and other whales, dolphins, and marine mammal fisheries examined as circumstances permitted. From this survey we were to decide on the most suitable area and methods for studying sperm whales in subsequent seasons. We were also to recommend which other marine mammal research projects in the area should be undertaken, either as part of our project or separately.We report here on the first field season. Because of the deadline (within two weeks of the end of the field work) the data has not been rigorously analysed, and we can give only the most basic results. However we hope that this report indicates that the study was successful within its objectives.},
keywords = {behaviour, dolphin, dolphins, Eubalaena glacialis, Fisheries, Humpback Whale, humpback whales, Indian Ocean, marine, marine mammal, megaptera novaeangliae, objectives, Oman, physeter, population, populations, sanctuaries, sperm whale, sperm whales, survey, whale, whales},
pubstate = {published},
tppubtype = {techreport}
}
The establishment of the Indian Ocean Whale Sanctuary in 1979 gave whale science an opportunity and a challenge: the opportunity to study protected whale; and the challenge to show that whale populations can be monitored purely through studies of living animals. The sperm whale (Physeter catodon), is commercially the most important, and the most numerous, large whale. It may be a significant link in the food web on account of returning nutrients from the deep ocean to the surface through its faeces. Analysis of the composition of sperm whale catches suggests that the sperm whale possesses a unique and interesting social system (Best 1979), a thorough knowledge of which is essential if these exceptional animals are to be properly protected.It was thus appropriate to carry out a study of the behaviour of the sperm whales in the Indian Ocean, principally using the methods developed on living right, grey and humpback whales, and the money raised by WWF-Netherlands. In order to obtain significant results it was thought necessary to have three field seasons of several months each.As very little was known of the whales of the Indian Ocean the first season consisted of a survey of those parts of the NW Indian Ocean which might have been suitable for studying sperm whales. During the survey methods of studying living sperm whales were to be developed, and other whales, dolphins, and marine mammal fisheries examined as circumstances permitted. From this survey we were to decide on the most suitable area and methods for studying sperm whales in subsequent seasons. We were also to recommend which other marine mammal research projects in the area should be undertaken, either as part of our project or separately.We report here on the first field season. Because of the deadline (within two weeks of the end of the field work) the data has not been rigorously analysed, and we can give only the most basic results. However we hope that this report indicates that the study was successful within its objectives.