Braulik,G.,Ranjbar,S.,Owfi,F.,Aminrad,T.,Dakhteh,S.M.H.,Kamrani,E.,Mohsenizadeh,F.
Marine Mammal Records from Iran Journal Article
In: Journal of Cetacean Research and Management, vol. 11, no. 334, pp. 49-63, 2010.
Abstract | BibTeX | Tags: abundance, bottlenose dolphin, Bryde's whale, Common dolphin, conservation, Distribution, dolphin, dugong, fin whale, Finless Porpoise, fishing gear, Gulf of Oman, Humpback Whale, humpback whales, incidental capture, killer whale, location, mammals, management, marine, marine mammal, Marine mammals, mortality, mysticete, mysticetes, Oman, Porpoise, Risso's dolphin, rough-toothed dolphin, Spinner dolphin, whale, whales
@article{,
title = {Marine Mammal Records from Iran},
author = {Braulik,G.,Ranjbar,S.,Owfi,F.,Aminrad,T.,Dakhteh,S.M.H.,Kamrani,E.,Mohsenizadeh,F.},
year = {2010},
date = {2010-01-01},
journal = {Journal of Cetacean Research and Management},
volume = {11},
number = {334},
pages = {49-63},
abstract = {A total of 114 marine mammal records of 14 species were compiled from Iranian coastalwaters of the Persian Gulf and Gulf of Oman. Eighty-one were from the Persian Gulf, 23from the Gulf of Oman and 10 were of unknown location. Records of finless porpoise(Neophocaena phocaenoides) (24), Indo-pacific humpback dolphin (Sousa chinensis) (22)and Indo-pacific bottlenose dolphin (Tursiops aduncus) (21) were by far the most numerousa probable reflection of their inshore distribution and local abundance. Other speciesrecorded were common dolphin (Delphinus capensis tropicalis), rough-toothed dolphin(Steno bredanensis), striped dolphin (Stenella coeruleoalba), spinner dolphin (Stenellalongirostris), Risso's dolphin (Grampus griseus), false killer whale (Pseudorca crassidens),sperm whale (Physeter macrocephalus) and dugong (Dugong dugon). Records of 24Mysticetes were compiled, 11 of which were tentatively identified as Bryde's whales(Balaenoptera edeni), three as Fin whales (Balaenoptera physalus), three as Humpbackwhales (Megaptera novaeangliae) and the remainder were unidentified. The largest threat tomarine mammals in Iran is likely to be incidental capture in fishing gear. Nine finlessporpoises were recorded as bycatch and this and other coastal species may be declining dueto unsustainable mortality rates. Other threats to the marine environment are discussed andrecommended marine mammal conservation and management small projects are described.},
keywords = {abundance, bottlenose dolphin, Bryde's whale, Common dolphin, conservation, Distribution, dolphin, dugong, fin whale, Finless Porpoise, fishing gear, Gulf of Oman, Humpback Whale, humpback whales, incidental capture, killer whale, location, mammals, management, marine, marine mammal, Marine mammals, mortality, mysticete, mysticetes, Oman, Porpoise, Risso's dolphin, rough-toothed dolphin, Spinner dolphin, whale, whales},
pubstate = {published},
tppubtype = {article}
}
Rajamani, L.
The conservation biology of the dugong (Dugong dugon) and its seagrass habitat in Sabah, Malaysia, a basis for conservation planning PhD Thesis
2010.
Abstract | BibTeX | Tags: conservation, dugong, GIS, habitat, Malaysia, Sabah, Seagrass
@phdthesis{,
title = {The conservation biology of the dugong (Dugong dugon) and its seagrass habitat in Sabah, Malaysia, a basis for conservation planning},
author = {Rajamani, L.},
year = {2010},
date = {2010-01-01},
journal = {Borneo Marine Research Institute},
number = {441},
pages = {315},
publisher = {Universiti Malaysia Sabah},
abstract = {Prior to 1999, dugongs were rarely observed in Malaysia. This first comprehensive
study of dugongs and their related seagrass habitats in Sabah, investigated the local
stakeholder environment, the abundance and distribution of dugongs, identified and
monitored threats to dugongs, and mapped seagrass habitats relevant to dugongs.
The study was conducted in two spatial scales namely, 1) Regional (to determine
dugong distribution in Sabah) (excluding Tawau) 2) Local - to determine local dugong
abundance, conduct seagrass mapping and community surveys at two study sites
Banggi island and Mantanani island. Community surveys consisted of a census,
interview surveys, a dugong monitoring programme and participant observation. This
information was used to determine stakeholder characters, and their perceptions of
the researcher, research project, dugongs and seagrasses. Local ecological knowledge
(LEK) of dugongs and seagrasses was also sought. The abundance, composition and
habitat area of seagrass was assessed using a method of visually estimating aboveground
seagrass biomass at sites along one kilometre transects perpendicular to the
coast. Biomass was estimated every 50 metres in shallow areas (up to 5 metres
depth) and every 100 metres in deep areas (greater than 5 metres depth). These sites
later form the basis of seagrass meadows using GIS applications. Standardised aerial
surveys were conducted regionally for the coastal waters of Sabah to determine
dugong distribution patterns. The communities of Banggi and Mantanani are
economically disadvantaged, practise destructive fishing and have little understanding
of ecological processes and concepts of conservation. However, the reasons for
dugong decline are known. Appreciation of the aesthetic value of dugongs within the
communities is varied. However, the community appears to have adequate local
knowledge of the dugong having cultural linkages through a dugong myth.
Approximately, 70% of the total population is young below the age of 30, who could
be receptive to new ideas. Outside influences from the media is widely available to the
community. The community is able to develop a relationship with the researcher and
participate cordially in research activities. Dugong numbers are very low in Sabah.
Fifty two dugongs were sighted in Sabah excluding Tawau. Based on these results,
crude estimates of minimal count are between 688 and 1376 dugongs residing in
coastal Sabah. Key dugong areas were identified to be Brunei Bay, Labuan Island, and
Sandakan Bay. Banggi Island and Mantanani Island supports a small population of
dugongs respectively. Based on this study, dugongs were subject to threats, which
were mostly anthropogenic. They were 1) blast fishing, 2) incidental entangling in nets
and 3) unsupervised tourism and vessel strikes. The number of mortalities in Sabah
(especially in Banggi Island), are high compared to dugong abundance results
obtained in this study. When Potential Biological Removal (PBR) estimates were
compared to crude estimates of yearly mortality, it is confirmed that dugong
populations are declining. Ten species of seagrass from two families were found in
Banggi Island and Mantanani Island. These include Halophila ovalis, Halodule uninervis
(broad and thin variety), Thalassia hemprichii, Cymodocea rotundata, Halophila
decipiens, Halophila spinulosa, Cymodocea serrulata, Syringodium isoetifolium, and
Enhalus acoroides. A new unidentified species of Halophila was collected in
Molleangan Island, west of Banggi Island. Approximately, 415 ha and 112 ha of
seagrass meadows were mapped in Banggi island and Mantanani island respectively
giving a total of 527 ha of seagrass available for dugong consumption. The
information obtained on the local communities, seagrass and dugong provided the
basis to inform a comprehensive conservation plan in Sabah. Key conservation
strategies include a dialogue and community education programme, provision of
alternative livelihoods, improving enforcement to prevent illegal fishing methods, comanagement
of dugong and seagrass resources, stringent controls on ecotourism and
vessel strikes, zoning of seagrass in marine protected areas and further research. As
the dugong is a migratory species, conservation management at an international level
with the neighbouring state of Sarawak, and countries of Brunei, the Philippines and
Indonesia is necessary.},
keywords = {conservation, dugong, GIS, habitat, Malaysia, Sabah, Seagrass},
pubstate = {published},
tppubtype = {phdthesis}
}
study of dugongs and their related seagrass habitats in Sabah, investigated the local
stakeholder environment, the abundance and distribution of dugongs, identified and
monitored threats to dugongs, and mapped seagrass habitats relevant to dugongs.
The study was conducted in two spatial scales namely, 1) Regional (to determine
dugong distribution in Sabah) (excluding Tawau) 2) Local - to determine local dugong
abundance, conduct seagrass mapping and community surveys at two study sites
Banggi island and Mantanani island. Community surveys consisted of a census,
interview surveys, a dugong monitoring programme and participant observation. This
information was used to determine stakeholder characters, and their perceptions of
the researcher, research project, dugongs and seagrasses. Local ecological knowledge
(LEK) of dugongs and seagrasses was also sought. The abundance, composition and
habitat area of seagrass was assessed using a method of visually estimating aboveground
seagrass biomass at sites along one kilometre transects perpendicular to the
coast. Biomass was estimated every 50 metres in shallow areas (up to 5 metres
depth) and every 100 metres in deep areas (greater than 5 metres depth). These sites
later form the basis of seagrass meadows using GIS applications. Standardised aerial
surveys were conducted regionally for the coastal waters of Sabah to determine
dugong distribution patterns. The communities of Banggi and Mantanani are
economically disadvantaged, practise destructive fishing and have little understanding
of ecological processes and concepts of conservation. However, the reasons for
dugong decline are known. Appreciation of the aesthetic value of dugongs within the
communities is varied. However, the community appears to have adequate local
knowledge of the dugong having cultural linkages through a dugong myth.
Approximately, 70% of the total population is young below the age of 30, who could
be receptive to new ideas. Outside influences from the media is widely available to the
community. The community is able to develop a relationship with the researcher and
participate cordially in research activities. Dugong numbers are very low in Sabah.
Fifty two dugongs were sighted in Sabah excluding Tawau. Based on these results,
crude estimates of minimal count are between 688 and 1376 dugongs residing in
coastal Sabah. Key dugong areas were identified to be Brunei Bay, Labuan Island, and
Sandakan Bay. Banggi Island and Mantanani Island supports a small population of
dugongs respectively. Based on this study, dugongs were subject to threats, which
were mostly anthropogenic. They were 1) blast fishing, 2) incidental entangling in nets
and 3) unsupervised tourism and vessel strikes. The number of mortalities in Sabah
(especially in Banggi Island), are high compared to dugong abundance results
obtained in this study. When Potential Biological Removal (PBR) estimates were
compared to crude estimates of yearly mortality, it is confirmed that dugong
populations are declining. Ten species of seagrass from two families were found in
Banggi Island and Mantanani Island. These include Halophila ovalis, Halodule uninervis
(broad and thin variety), Thalassia hemprichii, Cymodocea rotundata, Halophila
decipiens, Halophila spinulosa, Cymodocea serrulata, Syringodium isoetifolium, and
Enhalus acoroides. A new unidentified species of Halophila was collected in
Molleangan Island, west of Banggi Island. Approximately, 415 ha and 112 ha of
seagrass meadows were mapped in Banggi island and Mantanani island respectively
giving a total of 527 ha of seagrass available for dugong consumption. The
information obtained on the local communities, seagrass and dugong provided the
basis to inform a comprehensive conservation plan in Sabah. Key conservation
strategies include a dialogue and community education programme, provision of
alternative livelihoods, improving enforcement to prevent illegal fishing methods, comanagement
of dugong and seagrass resources, stringent controls on ecotourism and
vessel strikes, zoning of seagrass in marine protected areas and further research. As
the dugong is a migratory species, conservation management at an international level
with the neighbouring state of Sarawak, and countries of Brunei, the Philippines and
Indonesia is necessary.
Cockcroft, V.,Guissamulo, A.,Findlay, K.
Dugongs (Dugong dugon) of the Bazaruto Archipelago, Mozambique Technical Report
no. 72, 2008, ISBN: Final Report to SASOL Mozambique.
Abstract | BibTeX | Tags: abundance, Distribution, dugong, East Africa, Mozambique
@techreport{,
title = {Dugongs (Dugong dugon) of the Bazaruto Archipelago, Mozambique},
author = {Cockcroft, V.,Guissamulo, A.,Findlay, K.},
issn = {Final Report to SASOL Mozambique},
year = {2008},
date = {2008-01-01},
number = {72},
pages = {1-84},
abstract = {Historically, dugongs occurred in almost all coastal areas from southern Mozambique in the
west to Australia in the east, including many of the island States in the Indian and Pacific
Oceans between. However, through much of this range, dugongs have all but disappeared
and where they occur, are represented by relict populations. This is especially true for
Eastern Africa and the Indian Ocean and Mascerine Islands. In most areas dugongs have
been extirpated and only in southern, central Mozambique, the Bazaruto Archipelago, does a
relatively large number still survive.
Between April 2006 and December 2007 a series of 27 aerial surveys was flown over the
Bazaruto Bay region, from Cabo Sao Sebastio in the south to north of the Save River Mouth
in the north and between the coast and the 30 m isobath (extending to eastwards of the
Bazaruto Archipelago islands in the south). A total of 9052 nautical miles of survey was flown
during the 27 surveys. During these, 355 sightings of an estimated 760 dugongs were made.
Two core areas of distribution were apparent; a northern core region, between the Save River
Mouth and 21°24’ S, and a southern core region aligned with the shallow sandbanks to the
north and south of Santa Carolina Island. The mean group size of dugongs encountered was
2.22 and comparable to mean group sizes observed elsewhere. However, the maximum
group size observed was considerably smaller than those observed in other areas of dugong
abundance. Likewise, calculated dugong densities were substantially lower in the Bazaruto
area than they are in the Arabian Gulf or Australia. There was no evidence of any seasonal
variation in occurrence, group size, density or proportion of calves. The proportion of calves
was similar to that in other areas surveyed for dugongs.
Statistical manipulation of the data from aerial surveys suggests that the dugong population
inhabiting the area surveyed is around 250 animals.
The extent of dugong habitat was gauged by mapping seagrass occurrence, diversity and
distribution. Mapping was accomplished through extensive dive sampling of 982 stations
within the surveyed area, within 5m to about 25 m depth. Five species of seagrass were
identified within the area. These covered some 4.68 % of the area and occurred generally in
the north and close to the shore in waters less than 8 m deep. In the north, the areas of
greatest seagrass abundance and diversity coincide with the areas of greatest dugong
abundance. However, in the area to the north and south of Santa Carolina, seagresses were
almost absent, suggesting that this area is used by dugongs for reasons other than feeding.
Population Viability Analysis (PVA) modelling was used to assess the viability of the dugong
population in the Bazaruto Archipelago under various scenarios. PVA is a statistical method
of understanding the influence of a species’ natural history, in combination with demographic,
environmental, and random genetic (stochastic) events, on the dynamics of its future. The
species’ population dynamics is modelled as a set of discrete, sequential events (e.g., births,
deaths, catastrophes, etc.), which occur according to defined probabilities. Population
dynamics models provide a predictive tool, where the impacts of variables (threats), in this
instance – environmental threats (cyclones, floods); hydrocarbon exploration and incidental
fishing catch, can be theoretically modelled.
Overall, the PVA models suggest strongly that the dugongs inhabiting Bazaruto Bay are in a
precarious position and face extirpation. The models suggest that dugongs are particularly
susceptible to long term stressors that might reduce overall reproductive success. Further, the
analyses clearly show that regular deaths, from anthropogenic sources, are the major cause
of dugong decline.
A number of scenarios, covering options for hydrocarbon exploration and exploitation, are
presented and discussed, in terms of their potential impacts on the dugongs inhabiting the
Bazaruto area.},
keywords = {abundance, Distribution, dugong, East Africa, Mozambique},
pubstate = {published},
tppubtype = {techreport}
}
west to Australia in the east, including many of the island States in the Indian and Pacific
Oceans between. However, through much of this range, dugongs have all but disappeared
and where they occur, are represented by relict populations. This is especially true for
Eastern Africa and the Indian Ocean and Mascerine Islands. In most areas dugongs have
been extirpated and only in southern, central Mozambique, the Bazaruto Archipelago, does a
relatively large number still survive.
Between April 2006 and December 2007 a series of 27 aerial surveys was flown over the
Bazaruto Bay region, from Cabo Sao Sebastio in the south to north of the Save River Mouth
in the north and between the coast and the 30 m isobath (extending to eastwards of the
Bazaruto Archipelago islands in the south). A total of 9052 nautical miles of survey was flown
during the 27 surveys. During these, 355 sightings of an estimated 760 dugongs were made.
Two core areas of distribution were apparent; a northern core region, between the Save River
Mouth and 21°24’ S, and a southern core region aligned with the shallow sandbanks to the
north and south of Santa Carolina Island. The mean group size of dugongs encountered was
2.22 and comparable to mean group sizes observed elsewhere. However, the maximum
group size observed was considerably smaller than those observed in other areas of dugong
abundance. Likewise, calculated dugong densities were substantially lower in the Bazaruto
area than they are in the Arabian Gulf or Australia. There was no evidence of any seasonal
variation in occurrence, group size, density or proportion of calves. The proportion of calves
was similar to that in other areas surveyed for dugongs.
Statistical manipulation of the data from aerial surveys suggests that the dugong population
inhabiting the area surveyed is around 250 animals.
The extent of dugong habitat was gauged by mapping seagrass occurrence, diversity and
distribution. Mapping was accomplished through extensive dive sampling of 982 stations
within the surveyed area, within 5m to about 25 m depth. Five species of seagrass were
identified within the area. These covered some 4.68 % of the area and occurred generally in
the north and close to the shore in waters less than 8 m deep. In the north, the areas of
greatest seagrass abundance and diversity coincide with the areas of greatest dugong
abundance. However, in the area to the north and south of Santa Carolina, seagresses were
almost absent, suggesting that this area is used by dugongs for reasons other than feeding.
Population Viability Analysis (PVA) modelling was used to assess the viability of the dugong
population in the Bazaruto Archipelago under various scenarios. PVA is a statistical method
of understanding the influence of a species’ natural history, in combination with demographic,
environmental, and random genetic (stochastic) events, on the dynamics of its future. The
species’ population dynamics is modelled as a set of discrete, sequential events (e.g., births,
deaths, catastrophes, etc.), which occur according to defined probabilities. Population
dynamics models provide a predictive tool, where the impacts of variables (threats), in this
instance – environmental threats (cyclones, floods); hydrocarbon exploration and incidental
fishing catch, can be theoretically modelled.
Overall, the PVA models suggest strongly that the dugongs inhabiting Bazaruto Bay are in a
precarious position and face extirpation. The models suggest that dugongs are particularly
susceptible to long term stressors that might reduce overall reproductive success. Further, the
analyses clearly show that regular deaths, from anthropogenic sources, are the major cause
of dugong decline.
A number of scenarios, covering options for hydrocarbon exploration and exploitation, are
presented and discussed, in terms of their potential impacts on the dugongs inhabiting the
Bazaruto area.
Hines,E.,Adulyanukosol,K.,Somany,P.,Ath,L.S.,Cox,N.,Boonyanate,P.,Hoa,N.X.
Conservation needs of the dugong Dugong dugon in Cambodia and Phu Quoc Island, Vietnam Journal Article
In: Oryx, vol. 42, no. 386, pp. 113-121, 2008.
Abstract | BibTeX | Tags: aerial survey, conservation, dugong, education, location, management, marine, nets, population, survey
@article{,
title = {Conservation needs of the dugong Dugong dugon in Cambodia and Phu Quoc Island, Vietnam},
author = {Hines,E.,Adulyanukosol,K.,Somany,P.,Ath,L.S.,Cox,N.,Boonyanate,P.,Hoa,N.X.},
year = {2008},
date = {2008-01-01},
journal = {Oryx},
volume = {42},
number = {386},
pages = {113-121},
abstract = {This research was conducted to assess the location of population groups and conservation issuesaffecting dugongs Dugong dugon along the eastern Gulf of Thailand off Cambodia and Phu Quoc Island, Vietnam.Interviews in fishing communities in 2002 and 2004 along the Cambodian coast revealed that dugongs aresporadically found in fishing nets and their body parts are sold for a relatively large profit. During 4 days ofaerial surveys in Cambodia in 2004 we saw no dugongs. We interviewed villagers in Phu Quoc Island, Vietnam,in 2002 and learnt that dugongs are regularly found and hunted, again for high profits. In both countrieswe recommend that legislation addressing threatened species be strengthened and enforced. In collaborationwith the Cambodian and Vietnamese governments and NGOs, we propose the exploration of alternative nondestructivefishing methods and the initiation of an education campaign based on conservation of marinewildlife and the nearshore environment. National and transboundary management and community-based conservationare required in conjunction with strategies to address overfishing and poverty.},
keywords = {aerial survey, conservation, dugong, education, location, management, marine, nets, population, survey},
pubstate = {published},
tppubtype = {article}
}
Ross,J.P.
Recent marine mammal sightings in the Sultanate of Oman (1980-1981) Technical Report
no. 462, 1981.
Abstract | BibTeX | Tags: breeding grounds, cetacean, cetaceans, dugong, feeding, Humpback Whale, humpback whales, Indian Ocean, marine, marine mammal, Oman, sanctuaries, Strandings, whale, whales
@techreport{,
title = {Recent marine mammal sightings in the Sultanate of Oman (1980-1981)},
author = {Ross,J.P.},
year = {1981},
date = {1981-01-01},
journal = {Report presented to the special meeting of the IWC to plan a programme of scientific research on cetaceans in the Indian Ocean Sanctuary, Zeist, Netherlands.},
volume = {Document 23},
number = {462},
abstract = {This brief report summarises observations of live cetaceans, strandings and interviews with local fishermen. The source of sighting and stranding information is not always clear - stranded specimens referred to in this report were curated at the Zoological Museum in Amsterdam and the ONHM are also summarised in Gallagher 1991. JPR describes one stranding of a Dugong near Barka. He also describes Masirah fishermen's observations of a large whale with "bumps on its head like coffee cups" and long white flippers that they slap on the surface. He concludes that these are almost certainly humpback whales "migrating between summer feeding and winter breeding grounds. He also suggests that they were feeding on sardines which were abundant in the region during "these months" (although months not specified). Although he indicates that Oman's coast is abundant in food, yet tropical and thus suitable for breeding, he does not explicitly suggest that the humpbacks are year-round residents.},
keywords = {breeding grounds, cetacean, cetaceans, dugong, feeding, Humpback Whale, humpback whales, Indian Ocean, marine, marine mammal, Oman, sanctuaries, Strandings, whale, whales},
pubstate = {published},
tppubtype = {techreport}
}