Title: Sirenews
Full Citation
Permanent Link: http://ufdc.ufl.edu/UF00099157/00054
 Material Information
Title: Sirenews newsletter of the IUCNSSC Sirenia Specialist Group
Alternate Title: Siren news
Physical Description: v. : ; 29 cm.
Language: English
Creator: International Union for Conservation of Nature and Natural Resources -- Sirenia Specialist Group
Publisher: IUCN/SSC Sirenia Specialist Group
Place of Publication: Washington D.C
Washington, D.C
Publication Date: October 2010
Frequency: two no. a year[apr. 1984-]
Subject: Sirenia -- Periodicals   ( lcsh )
Marine mammals -- Periodicals   ( lcsh )
Genre: periodical   ( marcgt )
Bibliography: Includes bibliographical references.
Additional Physical Form: Also issued via the World Wide Web.
Dates or Sequential Designation: No. 1 (Apr. 1984)-
Issuing Body: Supported 1984-Apr. 1992 by the Species Survival Commission of IUCN, the U.S. Fish and Wildlife Service, and the U.S. Marine Mammal Commission; Oct. 1992 by the U.S. Marine Mammal Commission & U.S. Fish and Wildlife Service; Apr. 1993-Oct. 1994 by the U.S. Marine Mammal Commission; <Oct. 1995>- by the U.S. Marine Mammal Commission and Sea World, Inc.
General Note: Title from caption.
General Note: Latest issue consulted: No. 48 (Oct. 2007).
 Record Information
Bibliographic ID: UF00099157
Volume ID: VID00054
Source Institution: University of Florida
Holding Location: University of Florida
Rights Management: All rights reserved by the source institution and holding location.
Resource Identifier: oclc - 35841617
lccn - 2009208704
issn - 1017-3439

Full Text

ST )nAenew S
Newsletter of the IOCN Sirenia Specialist aroup

October 20o0 Funded by the U.S. Marine Mammal Commission Number 54





MOU ABU DHABI 4-6 October 2010

On 4-6 October 2010, the UNEP/CMS Office Abu Dhabi, with the support of the Environment
Agency Abu Dhabi (EAD) as the host and funding agency, held the First Official Signatory State Meeting of
the Memorandum of Understanding on the Conservation of Dugong and its Habitat throughout their Range
(Dugong MoU) at the Radisson Blu Hotel on Yas Island, United Arab Emirates.
The meeting served as the first official gathering of dugong range states and discussed a variety of issues
and potential solutions in relation to progressing positive conservation outcomes for dugongs across their global
range. Over 90 delegates, including representatives from the governments of 26 (out of 46) dugong range states
as well as technical experts, inter-governmental organizations, NGOs, and industry environmental managers
with an interest in dugong conservation, attended the meeting. Two Ministers (from Palau and Yemen) also
attended the Signatory State Meeting.
During the meeting, leading researchers including Professor Helene Marsh and other invited technical
experts, presented updated information on the conservation status of dugongs which highlighted the need to take
urgent actions if we are to conserve dugong populations in many range states. The delegates from dugong range
states had the opportunity to consider a range of novel and innovative management tools which have potential
to address key threats such as the incidental catch of dugongs in fishing nets, habitat loss and degradation,
illegal poaching and unsustainable customary take of dugongs.

p *Olms.ion SCommission de la sauvegarde des especes Species Survival Commission
Sirenews (ISSN 1017-3439) is published in April and October and is edited by
Cynthia R. Taylor, EcoHealth Alliance, 233 Third St. N., Suite 300, St. Petersburg, FL 33701 USA
James A. Powell, PhD, Sea to Shore Alliance, 200 Second Ave. S., #315, St. Petersburg, FL 33701 USA

Sirenews is available online at www.sirenian.org/sirenews.html

A dugong catch/incidental catch survey tool, developed by a group of technical advisors, has produced
some quality data from 20 countries in the Pacific Islands, South Asia and the United Arab Emirates. The data
will be combined into a geographical information system to identify the trouble spots, provide crucial
information on existing populations and map important habitat areas. In 2011, the survey will be extended to
range states in East Africa and the Western Indian Ocean littorals, Northwestern Indian Ocean, as well as South
Asian regions. Other solutions to protect valuable dugong habitat include establishing spatial closures as marine
reserves and temporal constraints to fishing operations. Incentives, such as loans for buying dugong-friendly
fishing gear, educational campaigns and measures to improve the livelihood of local communities were also
considered as a way to complement conservation efforts. Potential pilot projects will be developed to implement
these new incentive based tools, from which other marine species may benefit as well.
Through its commitment to the Dugong MoU, the EAD and UAE Government have taken the lead in
international efforts to conserve the dugong across its global distribution. Although much more work, effort and
funding will be required, this meeting made a substantial contribution toward ensuring the global conservation
of dugongs. The meeting concluded that the conservation strategy should address the need for greater protection
of marine biodiversity by combining different conservation tools. At the meeting, Bahrain, Palau, Seychelles,
Vanuatu and Yemen signed the CMS Dugong agreement bringing the number of signatories to 18. More
countries are likely to follow in the near future. The next Dugong MoU meeting is planned to take place in
2012. -Donna Kwan and Jenny Rennell (dkwan@cms.int; jrennell@cms.int)


As one of the first Signatory States of the UNEP Convention on Migratory Species of Wild Animals
(CMS)'s Memorandum of Understanding (MoU) for the Conservation and Management of Dugongs and their
Habitats throughout its Range, it was particularly apt that Madagascar played host to the first regional technical
meeting on this species. The meeting was held on 4-6 August 2010 at the Colbert Hotel in Antananarivo, with
government, UNEP/CMS and fisheries and wildlife management representatives in attendance as well as NGOs
currently engaged in dugong research. Representatives from the Environment Agency Abu Dhabi, the host
agency and sponsor to the Secretariat of the Dugong MoU, were also present at this significant event. After
three days of sharing information and brainstorming, the meeting was felt to be a resounding success by its
organizers and participants.
Opening speeches were given by the Honorable General de Brigade Herilanto Raveloharison, Minister
of the Environment, Forests and Water and Dr. Donna Kwan, the Program Officer from the UNEP/CMS
Dugong Secretariat in Abu Dhabi and the momentous event was broadcast on national television, raising
awareness about this elusive and highly endangered marine mammal, believed to be the source of the legendary
mermaid myth.
The Dugong MoU came into effect on 31 October 2007 after only 2 years of consultation with experts
and relevant officials from range state governments. A non-binding instrument, it seeks to conserve and protect
the dugong throughout its global range across over 40 range states. A number of range states including those
from the region have indicated interest in signing the Dugong MoU in the near future. In the lead-up to the First
Official Signatory State Meeting of the Dugong MoU (held in Abu Dhabi on 4-6 October 2010, see above), a
number of sub-regional projects were initiated, including the convening of technical workshops to support
dugong conservation efforts in range states and the implementation of the Dugong MoU.
The workshop, organized by Community Centred Conservation (C3), a non-governmental organization
now in its fifth year of dugong research and conservation in the western Indian Ocean region, saw
representation from the majority of range states in the region, including Comoros, Kenya, Madagascar,

Sire~ews No. 54

October 20100

Mayotte, Mozambique, Somalia, Seychelles and Tanzania. In fact, it was a historic occasion in that this was the
first ever dugong meeting attended by Somalia. Of all the sub-regions of the Dugong MoU, this region is the
one with the highest number of signatories, perhaps in recognition of the degree to which this species is
threatened with extinction in the waters of the western Indian Ocean.
After decades and in some cases, centuries, of intensive hunting for its tasty meat, the dwindling
remnants of dugong populations number only handfuls of individuals around small island groups and just
hundreds off eastern African states. Clinging precariously to the coastlines where their sole source of food,
seagrass, grows, they are frequently entangled in artisanal gill nets, currently the greatest threat to their
The main barrier to dugong conservation in East Africa and the West Indian Ocean islands is the lack of
technical and financial capacity to implement suitable actions. The Dugong MoU Conservation and
Management Plan (CMP) for dugongs in the West Indian Ocean now provides a framework to progress
conservation and management actions in this region. This meeting provided a vital opportunity for the countries
to present updates on the status of their dugong populations and associated habitat, as well as to seek grounds
for future collaboration in the fields of both research and management. Furthermore, in-depth analyses were
conducted on the current financial and technical capacities of range states to implement dugong research and
conservation activities.
The UNEP-CMS Standardised Survey methodology was presented and explained in detail and will be
launched in various countries in early 2011, supported in part by small grants provided via the Secretariat and
administered by C3. The surveys will help to identify key dugong habitat, population numbers and trends, and
impacts including direct harvest, habitat degradation and fisheries by-catch. Since the methodology is
questionnaire-based it is sufficiently flexible and low-cost to be adapted regionally and will yield comparable
data, to be housed by the Secretariat in its coordinating role. The survey and an accompanying Project Manual
can be downloaded from the Secretariat's website at
http://www.cms.int/species/dugong/dugongnoticeboard.htm under the relevant notices posted. The meeting
report with details of discussions and presentations will be available from the same site later this month.
C3 has been generously supported via the BP Conservation Leadership Programme since the inception
of its first community-based dugong research in the western Indian Ocean in 2006 and more recently by the
CMS Dugong secretariat. -Patricia Z.R Davis, (Community Centred Conservation (C3), www.c-3.org.uk)

Madagascar Meeting Participants

Sireviews No. 54 October 202-0

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Manatee Subspecies Genetically Confirmed, But Diversity Challenge Looms: Two Belize Populations
Offer Opportunity in a Desert of Genetic Diversity
Gainesville, FL The first genetic study to compare nuclear DNA of endangered Antillean manatees in Belize
with Florida manatees confirmed their designation as separate subspecies. Belize's manatees, however, were
found to have extremely low genetic diversity, raising questions about their long-term genetic viability.
The Central American country of Belize hosts the largest known breeding population of Antillean manatees and
is touted by biologists for its potential to repopulate other parts of Central America where manatees are severely
reduced, rare or absent.
"It turns out that the genetic diversity of Belize's manatees is lower than some of the classic examples
of critically low diversity" said U.S. Geological Survey (USGS) conservation geneticist Margaret Hunter,
Ph.D., who led a molecular DNA study of genetic diversity in the Antillean subspecies in Belize.
Belize's Antillean populations scored lower in genetic diversity than textbook examples of"bottlenecked"
endangered species such as Wanglang giant pandas, the East African cheetah and an island koala population
founded by only three koalas.
Endangered species need genetic diversity to weather threats to their survival, including random or rare
shocks such as disease, hurricanes or habitat destruction. When a population drops to low numbers, the diversity
of its gene pool also shrinks. Even after it rebounds to greater numbers, that population decline leaves a legacy
of reduced genetic diversity known as a bottleneck. This renders the population more vulnerable to future
shocks, explained Hunter.
The low genetic diversity in Antillean manatees is attributed, in part, to centuries of hunting that were
only curtailed early in the 20th century. Once found throughout coastal regions of Central and South America,
Antillean manatees are now rare or absent in parts of Central America where they used to be considered
abundant. Today, even Belize only hosts about 1,000 individuals a number well below the threshold
recommended for long-term sustainability, said Hunter.
Distinct Populations Offer Opportunity
Although the study found low overall genetic diversity in Belize, notable differences were found in
manatees that live near Belize City compared to manatees living in lagoons, rivers, and cayes farther
south. These differences, said Hunter, equate to genetic variation, which is valuable for sustaining a diverse
gene pool.
"When it comes to the sustainability of a species, this is the type of genetic diversity you want to
preserve for the future," explained Hunter.
To sustain the diverse gene pool these populations offer, managers will need to consider methods of
enabling natural migration and mixing to take place between the two populations.
"These results show the importance of corridors of suitable habitat and low human impact that allow
manatees to travel between key sites," said co-author Nicole Auil Gomez, a Belizean biologist who does
consulting for the Florida-based conservation organization Sea 2 Shore Alliance. "Leaving pockets of habitat is
no longer enough," she added.
Confirmation of the Subspecies
The genetic evidence that Florida manatees (Trichechus manatus latirostris) are not regularly mixing
with populations of Antillean manatees (Trichechus manatus manatus) in Belize means they don't naturally
affect each other's population size or genetic diversity, Hunter said.
The question of whether these two seemingly distant populations were interbreeding had been raised in
light of radiotracking evidence that manatees are capable of migrating long distances. Florida manatees have
turned up in places as far as Rhode Island, the Bahamas and Cuba.

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October 20100

The only prior genetic data comparing the subspecies came from mitochondrial DNA, which is useful
for understanding historical relationships on an evolutionary time scale (think millennia, not decades). By
including nuclear DNA, this study provided a modern-day assessment of whether the two populations are
migrating and interbreeding.
"We are continuing to piece together the genetic relationships of manatees throughout the Caribbean and
it's giving us insights into how to maintain healthy and stable populations," said USGS biologist and co-author
Bob Bonde, Ph.D.

Article Citation: M. E. Hunter, N. E. Auil Gomez, K. P. Tucker, R. K. Bonde, J. Powell, and P. M. McGuire.
2010. Low genetic variation and evidence of limited dispersal in the regionally important Belize manatee.
Animal Conservation. Published online in advance of print. http://onlinelibrary.wiley.com/doi/10.1111/j. 1469-


Approximately 30 institutions involved in manatee research, conservation, education and protection met in
Itamaraca Island (NE Brazil) on 22-24 March 2010, in a workshop to review the country's action plan for
sirenians. Including both species present in Brazil, the West Indian (T. manatus manatus) and Amazonian (T
inunguis) manatees, the National Plan for the Conservation of Sirenians was officially approved and published
on 1 September through Portaria ICMBio 84/2010.


As a result of a 2-day (9-10 Sept 2010) workshop in Belem, PA, Brazil, over 15 institutions committed
to research, education and protection of aquatic mammals, and agreed on implementing a concerted response to
strandings and fishery-related events involving aquatic mammals in the northern region of Brazil (REMANOR).
In October, all four regional groups (from SE, S, N and NE Brazil, the latter established 12 years ago) shall
officially compose the Brazilian stranding network (REMAB). Manatee calves are the subject of disturbingly
numerous stranding events, both in coastal and wetland areas.


Fundagco Mamiferos Aquaticos and Instituto de Desenvolvimento Sustentavel Mamiraua are organizing
a workshop on manatees to take place 25-26 October 2010. The aim is to discuss strategies to prevent and deal
with the growing number of rescued manatee calves (the result of intentional capture with harpoons or
incidental entanglement in fishing nets). All institutions dealing with the issue now or in the past are being
invited to the event, which will take place during the 8th Congress of the Latin American Society of Experts on
Aquatic Mammals to be held in Florian6polis, SC, 25-28 October.



Distribution and abundance of dugong (dugon dugon) in the Kimberly Region, North Western Australia
from 1995 to 2005. Dugong distribution on the Kimberley Coast of Western Australia has not been formally
surveyed and there are no published data records or even anecdotal information on this aspect of dugong

Sireytews No. 54

October 20100

activity. In this study, I report sightings made by Australian Customs observers during routine surveillance
flights. Data on survey effort is unavailable, due to the classified nature of Customs activities. However, their
input is sufficient to show that dugongs are present throughout the coastline from Broome to the Northern
Territory border and their presence was observed throughout the year. Sightings were also made regularly at the
offshore reefs across deep ocean stretches in excess of 200km from other habitat. Data is also presented on
indigenous hunting in the region. There is a clear necessity for quantitative information to assess the relative
importance of the region to the nation's dugong population and to determine the sustainability of their hunting


The dugong is widely distributed in the tropical areas of the Pacific and Indian Oceans. This species has
been listed as vulnerable to extinction by the IUCN (2006) and their population is severely depleted in most
countries where they are found (Marsh et al., 2002) due to the impact incurred by increased hunting, boat traffic
and habitat destruction. Northern Australia has often been cited as the last stronghold for the species, as the
range of dugong stretches from Moreton Bay in Queensland to Shark Bay in Western Australia; an area with
relatively little human population or coastal development. In Australia a number of surveys have been
undertaken to assess the distribution and abundance of dugongs, along with any threats to its survival. These
have covered the entire Queensland coastline (Marsh et al., 2002), parts of the Northern Territory coastline
(Bayliss & Freeland, 1989), and much of the central areas of Western Australia, including Shark Bay, Ningaloo,
Exmouth and Pilbara Coast (Gales et al., 2004).
Some of these surveys suggest that the dugong population may be under threat in the relatively
developed areas on the East Coast, where a significant decline in dugong numbers has been reported (Smith &
Marsh, 1990). In fact, current estimates show that the present rate of indigenous hunting in the Torres Strait
Islands is unsustainable. In most other countries where dugongs are found, they are subjected to multiple
sources of man-induced mortality and habitat damage (Heinsohn & Marsh et al., 2004).
Despite the comprehensive knowledge of dugongs for most of their range in Australia, an insufficient
knowledge base of distribution exists on the coast of Western Australia between Broome and the Northern
Territory borders. No formal survey has been undertaken in this remote and thinly populated region, despite its
likely having a significant dugong population and being cited as the highest priority for dugong research in
Western Australia (Marsh et al., 2002). This paper seeks to partially redress our limited knowledge of the
dugong populations using data composed by the Australian Customs Services.
In addition, information on dugong harvesting by three aboriginal communities between Broome and
One Arm Point, in far Northwestern Australia, have been obtained through personal observation. I resided
within the Badi Aboriginal Community in order to assess if there was a threat posed to the dugong population
by harvesting activities.


Aerial Surveys
As dugongs feed in shallow water, aerial surveys are the most feasible method of determining their
distribution and abundance (Marsh & Sinclair, 1998). While formal standardised surveys such as those
conducted by Marsh & Sinclair (1998) are ideal, at the time of writing only a limited amount of investigative
procedures have been carried out, perhaps because of the logistical difficulties and inadequate financial
resources available for surveying such a remote region. Consequently, this study uses non-quantitative data.
The sightings data was collected by observers from the Australian Government Coast Watch program
supplementary to their primary surveillance task. The latter involves regular flights using a Pilatus Britten-

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October 20100

Norman Islander aircraft, modified for their work, with enlarged bubble windows, gyroscopically stabilized
binoculars and cameras for observers seated on each side of the aircraft and additionally an integrated laptop
computer to record sightings. These flights are carried out at relatively low altitudes and follow a variety of
routes. Unfortunately, the flight paths are classified for security reasons and I am thus unable to assess spatial
It is not possible then to say whether the absence of dugong sightings in an area indicates their true
absence or rather low/no survey effort over a specific area. Accordingly, I cannot make quantitative
comparisons over time or space.
The coastline considered in this study runs in a broadly northeasterly direction between Broome in
Western Australia (170 57'S and 122 14E) and Joseph Bonaparte Gulf on the Northern Territory border (12
16'S and 128E). The shoreline is deeply indented by large shallow inlets and bays and covers a lineal distance
of about 1,300 km. Many small islands are scattered along its length at distances of up to 20km from the
shoreline. The sea bottom in this area is largely composed of muddy sand with a gentle gradient. As a result,
the area supports the growth of seagrass, which is essential to support a significant population of dugongs (Lal-
Mohan, R.S., 1993)

Indigenous Knowledge

The Aboriginal population on the Dampier Peninsula is estimated at 4,200 (Aboriginal Land Council,
Broome, 2007). Approximately 300km north of Broome, along the Dampier Peninsular at latitude (160
30'south), "traditional" aboriginal communities are found at One Arm Point, Djaridjan and Lomabadina
(Figurel). Both Djaridjan and One Arm Point are the home to Badi and Jawi communities. Their predecessors
have exploited this environment with its huge tidal range (9. 1-m) for thousands of years. The people in these
communities have strong interrelationships between one another and with the Moamjum people of Derby.
The Badi community hunt the dugong on a regular basis in the dry season, between April and October. Sunday
Island, east of One Arm Point, is a sacred site for the men of the community. A powerful tidal current surges
through the bay entrance of the Island, causing whirlpools and cross currents. The hunters from One Arm Point
enter and leave only during the change of tides.
The dugong meat forms a significant part of the diet of indigenous people in the region, along with fish,
turtles, shellfish, clams and crabs. As in many hunter/gatherer societies, the hunter sees the dugong not just as a
food source, but as an element important in cultural, spiritual and social practices. For these reasons, its meat is
commonly distributed between communities on the Dampier Peninsular where it is shared between families.
John Kernot, who operated the bush taxi services from Broome to One Arm Point for 20 years, regularly
transported dugong meat to these communities. Occasionally the meat is flown to Derby from One Arm Point,
particularly when a death occurs in the community. On the contrary, a report to Cairns Fisheries Queensland
indicates that those traditions had broken down to the extent that "commercial" hunting for dugong meat and
teeth is practiced. However, there is no hard evidence to support the view that such activity is conducted in the
region surveyed here.
Although Broome has a transient indigenous population, only one group, the Hunter family, hunt
dugong in Roebuck Bay, Broome. This shallow bay is a favorable habitat for dugongs because of the abundance
of seagrass, which is their primary food source. Their feeding trails are commonly seen when the bay is covered
with water. However, in this relatively developed area, more dugongs are killed due to their exposure to human
activities such as boating, cargo vessel movements and fishing rather than by indigenous hunting (the late
"Dicko" Hunter, dugong hunter, pers.comm.)
Within this study, the Bardi community on the Dampier Peninsula are by far the most active in hunting
the dugong. For this reason, input from John Kernot (bush taxi driver), Bruce Wiggan (Aboriginal), and others
was sought in estimating the harvesting of dugongs in this area over the period 1996 to 2005.

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October 20100

Figure 1. Map of Dampier Peninsula, W.A. (source: Rouji et al., 2003).

o Distribution of dugong meat from 1996 to 2005 (J. Kernot) by
.... Bush Taxi, Broome to One Arm Point, a distance of 250km

---- Flight route from Broome to Derby where dugong meat is
transported by the Badi Aboriginal community for ceremonies

Boats to Sunday Island, from One Arm Point, W.A.

Roebuck Bay, Broome. (bottom left of map)

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40 -1- I
20- -

199 199 199 199 200 2001 200 200 200 200

Figure 2. Estimated number of dugong harvested from the Dampier Peninsula Western Australia

Results of Indigenous Catch Estimates
I have combined dugong catch estimates from four locations of the Dampier Peninsula Beagle Bay, One
Arm Point, Lombadina and Cape Laveque, from 1996 to 2005 (Figure 2). Between April and October 1999,
dugongs were hunted in large numbers by the Badi community from One Arm Point. It is estimated that about
four dugongs per week were killed during this season, giving a total take of 120 mammals. There was no
explanation as to why the harvesting carried out in this period of 1999 was excessive. This additional hunting
activity was confirmed by the observation of Australian Custom Observers during their flights over the area,
and the transport of dugong meat to other communities by bush taxi (J.Kernot, pers. comm.). During the 2002
hunting season, the community experienced severe social problems which have had an impact on hunting
trends. The following season saw a significant decline in hunting activities which occurred when a take-away
food establishment was built in Broome 2003.
Whether the present take is lower or higher is difficult to assess. On the one hand, contact with
Europeans has probably reduced the frequency of hunting activities; however, the use of power boats has
probably increased the efficiency of the hunters. Nonetheless, the average figure of approximately 38 dugong
per annum based on the data in Figure 2 probably overstates the likely take in the future.
The social problems of the communities in this survey seem to be typical episodes in the collision
between European and Indigenous cultures in many areas of Australia. Experience has demonstrated that
continued contact between the two cultures invariably leads to gradual abandonment of traditional ways by the
indigenous people. In the present case, it seems highly likely that the taking of the dugong by indigenous
communities will diminish over time for this reason.
However, more importantly, studies by Dr Rouji et al. (2003) have shown that some of the Badi
aboriginal people who have moved away from western diets and returned to traditional marine foods have
experienced beneficial effects on their health.

Australian Coast Watch Aerial Surveys
The area surveyed by Australian Coast Watch was approximately 3,500klm between Broome and the
Northern Territory border which represents 9.89% of the Australian Coastline. At much greater distances from
the coast, a number of offshore reefs encompass shallow lagoons which support seagrass (Aust. Coast Watch).
Their data showed that these areas have dugongs present.
234e3ew No,5,Otoe,_0

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October 20100

Flights were conducted January through December each year, with an average of 2.2 dugongs sighted
per flight per month. On average, most dugongs per flight were sighted in January with 3.2 individuals,
followed by May with 3.1 and March with 2.6 dugongs sighted (Figure 4). Eight dugongs (1.2%) were
identified as calves, with calf sightings recorded in the months of January (1996, 1997, 1998), February and
August (1998), and July (2002).
Calf numbers and group size recorded by Customs are purely approximations and discrepancies were
inevitably present, largely due to the fact that dugong observations were of secondary significance as the
primary activities carried out by customs personnel is aerial surveillance from a range of various altitudes.
The size of dugong groups sighted ranged between one and 22 individuals, with an average group size of
5.5 animal; 189 dugongs (27.6%) were sighted as solitary animals, 110 (16%) in pairs, 66 (9.6%) in groups of 3,
222 dugongs (32.4%) in groups of 4 to 9, and 99 dugongs (14.4%) in groups of 10 and above (Figure 5). Groups
of 21 were recorded on two occasions, in January 1996 and May 2000, both in the vicinity of the Bonaparte
In the region, 686 dugongs were sighted between Broome and the Northern Territory border (18S and
128 E) by Australian Customs, surveyed between 1995 and 2005.

Figure 3. Number of dugongs sighted from 1995 to 2005.

Sireviews No. 54 October 202-0





Z 40


1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005

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October 2010

E 2.5

0 1.0
> 0.5


C* .~ .

Jan Feb Mar

Apr May Jun Jul Aug Sept Oct Nov Dec

Figure 4. Average number of dugongs sighted per flight per month

200 ,
C 120 16%
b 80 9.6% 8%
0 ---_ _% -779W ---- ------- ----------- ---------
z 60 6.4% 6.1
40 A4.1% 4.7% 4.4%
20 1.3%70
1 2 3 4 5 6 7 8 9 10 12 15 21
Group size

Figure 5. Number of dugongs sighted in group sizes from 1-21 animals.

No wide-ranging study has occurred in the region of the northwest Kimberly on the distribution and
abundance of dugongs. The remoteness of the area, an Archipelago of islands, and the distances between the
reefs and the coastline contribute to the lack of knowledge about the range covered by individual mammals. The
tidal range along the Kimberley coast varies from 9 to 10 metres and the sea bottom has a gentle slope. The
result is very rapid tidal currents which make harvesting by the indigenous community (with a traditional canoe)
difficult and often dangerous. Powered boats are used today which have reduced these problems. However,
certain areas are inaccessible and cannot be easily reached, except at the turn of the tide.
I have shown in Figure 2 that harvesting by Aboriginal communities, in far north Western Australia,
may possibly be sustainable where the average take is at a bare minimum. The baseline is appropriate

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October 2010

management by the community. However, in comparison to the Torres Strait and Cape York Peninsula
communities, over-harvesting of the dugong indicate that it is unsustainable. (Heinsohn et al., 2004).
It is noteworthy that Bardi indigenous hunters have reduced their harvesting from 2003, owing to a
population movement to Broome and Derby. Coast watch surveys over the 1995 to 2005 decade reveal that the
Dampier Peninsula, north of Broome, is known to support a sizeable population of dugongs even though some
dugongs may return to the same geographical location between flights by customs. On the other hand, a more
accurate survey in the future could substantiate that the sizable numbers of dugongs could be greater than Shark
Bay, surveyed by Holley et al., 2006. In 2008 a decision by the federal government to construct an L.N.G.
processing plant in the Kimberly region will undoubtedly have a significant and irreversible impact on this
marine environment. There are large areas of seagrass in the location where large container vessels could
potentially cause turbulence to the sea beds and destabilize this ecosystem. The other area of vulnerability is
illegal fisherman, operating in areas which are relatively remote from the Australian coastline such as Ashmore
Reef, due north of Broome which is outside the range of indigenous hunting. In general, Indonesian fishermen
capture mainly shark for their fins, Trochus shells and some turtles. It is apparent that Indonesian fishermen are
using dugong as bait to catch dwindling stocks of sharks (Western Australian, 16/8/ 2006 p. 1). Hopefully,
activities by the Coast Watch program will adequately protect dugong populations, along with those of many
other marine species on offshore reefs.

Summary and Conclusions
The data on the distribution and abundance of dugongs around the waters of the Kimberley coast has
clearly provided useful information for research in the future. It may be that systematic counts of dugongs over
a period of years could provide more reliable and specific data on this elusive mammal. It is difficult to assess
the status of dugongs in such remote locations as the Kimberley; however Australian Customs have played a co-
operative role in assisting me to compile the dugong population data. At this point, it must be noted that the
sons of the families that hunted the dugong at various locations now reside in Broome and Derby and are part of
a modem cosmopolitan society. Hunting by the local aborigines still occurs; however, their culture is
diminishing as a new direction is emerging from their tribal and traditional customs. Whether this trend
continues can only be determined by the communities who live around the Kimberley coast.
In my opinion, the Western Australian coastline is unique at present in relation to the dugong. It appears
that the aboriginal communities of the Kimberley coast have demonstrated the obvious benefits of co-
management. I view, with a considerable degree of concern, that this established practice as applied by the
existing communities could be significantly impacted by western influence and ignorance of the sensitivity of
this unique marine environment and ecosystem.

I would like to thank the following: Australian Customs Services, Broome Western Australia; Customs
Dept. Canberra; Bruce Wiggan, aboriginal community resident of One Arm Point; Wally Wiggan and his
navigational skills among the turbulent waters of King Sound, in addition to his ability to track dugongs and
hunt them traditionally for his community; Roy Wiggan, Elder of the Bardi Community, gave authorization to
enter Badi country; John Kumot, transport driver (bush taxi) for aboriginal communities of One Arm Point,
Beagle Bay, Djaridjin and Lombadina, who collected data on hunted dugongs which he transported to
aboriginal communities; Dept of Coastal Valuations Section in Canberra; the late Dicko Hunter for his
knowledge on dugong hunting in Roebuck Bay, Broome; Dr. Ivan Lawler, James Cook University, whose
patience and time was invaluable; and Brigitte Sommer, Southern Cross University, for her outstanding ability
with statistics. -Sylvie Annie Adam (sylviaadam@hotmail.com)

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Anderson, P. K. 1986. Dugongs of Shark Bay, Australia Seasonal Migration, Water Temperature and Forage National Geographic
research, vol 2, (4): 473-490.

Bayliss, P., Freeland, W.J. 1989. Seasonal Distribution and abundance of dugongs in the Western Gulf of Carpentaria. Australian
Wildlife Research 16, 141-149.doi:10.1071/WR9890141.

Gales, N., McCauley, R.D., Lanyon, J., Holley, D. 2004. Change in abundance of dugong in Shark Bay and Exmouth Gulf, Western
Australia, evidence for large-scale migration Wildlife Research No 31 P283-P290.

Greenwood, M.P. 1926. Australia's Wildlife Wonderland National Geographic Magazine June, P.329 -356.

Heinsohn, R., Lacy, R.C., Lindenmayer, D.B. Marsh., H., Kwan, D. K., and Lawler, I. R. 2004. Unsustainable harvest of dugongs in
Torres Strait and Cape York (Aust.) waters two case studies using population viability analysis. Animal Conservation 7, 417-42.
Holly, D.K., Lawler. I.R., Gales. N.J., Summer., 2006. Survey of Dugong distribution and abundance in Shark Bay. Reveals additional
key habitat area. CSIRO Publishing, Wildlife Research, No.33, p243 to 250.

Kwan, Donna. 2005. Traditional Use in Contemporary Ways: The management Challenge of a Sustainable Dugong Fishery in Torres
Strait. Senri Ethnological Studies 67: 281-302.

Lal-Mohan, R. S. 1993. Status of Seagrass Beds and Dugong of the Indian Coast. Conservation Indian Journal of Fisheries. India.

Love, John. 1963. Stone Age Bushmen of Today. 1930, Worrora Aboriginal Community. Nature Coast.

Marsh, H. & Lawler, I. 2002. Dugong distribution and abundance in the Northern Great Barrier Reef Marine Park. GRUMPA
Research Pub. 77.

Marsh, H., Sinclair D.F. 1998. Correcting for visibility bias in strip transect aerial surveys Aqua Fauna. Journal Wild Management 53
(4): 1998.

Marsh, H., Sinclair D.F. 1989. An Experimental evaluation of dugong and sea turtle aerial survey techniques, Australian Wild. Res. 16:
639 -650.

Marsh, H. 1998.,Torres Strait Dugong and Fishery Assessment Report.

Marsh, H., Saalfield., W.K. 1990. The Distribution and Abundance of Dugong in the Great Barrier Reef. Marine Park, South of Cape
Bedford. Aust. Wild. Res. 17.

Marsh, H. Arnold, P. 1989. Endangered and charismatic Megafauna James Cook University.

Marsh, H. Eros, C. Corkeron, P. Breen, B. 1999. The Dugong in Australia, A Conservation and Overview. James Cook University,
Townsville. Qld.

Marsh, H., I. R. Lawler, D. Kwan, S. Delean., K. Pollock., and M. Alldredge. 2004. Aerial surveys and the potential biological
removal technique indicate that the Torres Strait dugong Fishery is unsustainable. Animal conservation, 435- 443). Zoological
Society, UK.

Preen, A.R. Marsh, H. Lawler, A.L. Prince, R.I.T. Shepard, R.. 1997. The Distribution of Turtles, Dolphins, and other Megafauna in
Shark Bay Ningaloo Reef, and Exmouth Gulf, W.A Wildlife Research. 24, p185 to 208.

Prince, R.I.T 1999. Dugongs in the Northern Waters of Western Australia, Technical Report No7, CALM.

Prince, R.I.T., Anderson., P.K. Blackman., D. 1981. Status and Distribution of dugong in Western Australia. In H. Marsh (ed.) the
Dugong. Seminar and Workshop. James Cook University, Queensland.

Sirenews No. 54 13 October 2010

Rouji, P.M. Dewailly, E. Blanchet, C. 2003. Fat, Fishing Patterns, and Health among the Bardi People of North Western Australia.
Lipids, Vol. 38 no.4

Smith, A. Marsh, H. 1990. Management of Traditional Hunting of Dugongs in the Northern Great Barrier reef, Australia.
Environmental Management, Vol. 14, No.1 p.p. 47-55

Sheppard, J.K. Preen, A.R Marsh, H, Lawler, I.R. Whiting, S. D. Jones E.R. 2006. Movement Heterogeneity of Dugong over large
Spatial Scales. Journal of Experimental Marine Biology and Ecology 334, 4-83.

Stokes, T. 2004. Report of a workshop on future aerial surveys for dugong in Queensland and the Torres Strait. CRC Reef,
Townsville, Qld.

Tager, J. 1999. Going Going Dugong, Earth Island Journal.


The presence of the manatee in Tapajds River, state of Pard, Brazil. Recently a photograph of a manatee
(Trichechus inunguis) was published by Greg Grandin (Grandin, 2009: 283) portraying a specimen probably
collected in the 1930's in Fordlandia, right bank of Tapaj6s River. This picture belongs to the archives of the
Benson Ford Research Center at The Henry Ford and is perhaps the southernmost reference of this species in
that river.
I have visited the lower Tapaj6s River several times since 1991, and have assembled fisherman records
regarding the presence of the "peixe-boi" from the following localities: Irucanga (02035'S, 5458'W); Cajutuba
(02040'S, 55000'W); Maguari (02047'S, 55001'W) (December, 1991); Aveiro (03036'S, 55019'W); Fordlandia
(03050'S, 55030'W) (January, 1992); lago Jurucui (02033'S, 54058'W); Piquiatuba (02059'S, 55005'W)
(January, 1993); Tauari (03003'S, 55007'W) (February,2007); and Aramanai (02042'S, 55000'W) (April, 2010).
On 1 June 2010 one young specimen was found in Porto Novo (02037'S, 54058'W) by local people, and
forwarded to the Intituto Chico Mendes de Conservacgo da Biodiversidade (ICMBio).
Alfonso Maria Olalla (1899-1971) can be considered the greatest collector of mammals and birds of the
Amazonian Basin. Between 1922 and 1969 he assembled thousands of specimens which are currently housed
in several museums around the world. Concerning T. inunguis, he collected specimens in some localities from
both banks of the lower Tapaj6s. In the American Museum of Natural History, New York, there are specimens
collected in August 1931 in Santarem (02026'S, 54042'W) (AMNH 95765, 95766, 95767, 95768) and Inajatuba
(02052'S, 55010'W) (AMNH 95763, 95764). In the Museum of Comparative Zoology, Cambridge, there is a
specimen (MCZ 31767) from Tauari obtained in October 1932.
The capture of specimens occurs accidentally in fishnets of local people. The greatest threat to T. inunguis
seems to be, nevertheless, the contamination of waters by mercury remains of gold mining activities
("garimpos") in localities along the tributaries of the upper Tapaj6s. Studies about the presence of mercury in
fish and human communities confirm the problem in the area (Malm et al, 1995; Lebel et al, 1997; Bidone et al,
1997; Roulet et al, 1998; Dolbec et al, 2000). S. M. Vaz (Museu Nacional, Universidade Federal do Rio de
Janeiro, Secgo de Mamiferos, 20940-040 Rio de Janeiro, RJ, Brazil. E-mail: smvaz@mn.ufrj.br


Bidone, E. D., Castilhos, Z. C., Cid de Souza, T. M. & Lacerda, L.D. 1997. Fish contamination and human exposure to mercury in the
Tapaj6s river basin, Parl state, Amazon, Brazil: A screening approach. Bulletin of Environmental Contamination and
Toxicology 59(2): 194-201.
Dolbec, J., Mergler, D., Sousa Passos, C. -J., Sousa de Morais, S. & Lebel, J. 2000. Methylmercury exposure affects motor
performance of a riverine population of the Tapaj6s river, Brazilian Amazon. International Archives of Occupational and
Environmental Health 73(3): 195-203.

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Grandin, G., 2009. Fordlandia: The rise and fall of Henry Ford's forgotten jungle city. New York, Metropolitan Books, Henry Holt
and Company, xiv+416 p.
Lebel, J., Roulet, M., Lucotte, M. & Larribe, F. 1997. Fish diet and mercury exposure in a riparian Amazonian population. Water, Air
and Soil Pollution 97(1): 31-44.
Malm, O., Branches, F. J. P., Akagi, H., Castro, M.B., Pfeiffer, W.C., Harada, M., Bastos, W. R.& Kato, H. 1995. Mercury and
methylmercury in fish and human hair from the Tapaj6s river basin, Brazil. The Science of the Total Environment 175(2):
Roulet, M., Lucotte, M., Canuel, R., Rheault, I., Tran, S., DeFreitos Gog, Y. G., Farella, N., Souza do Vale, R., Sousa Passos, C. -J.,
De Jesus da Silva, E., Mergler, D. & Amorim, M 1998. Distribution and partition of total mercury in waters of the Tapaj6s
river basin, Brazilian Amazon. The Science of the Total Environment 213(1):203-211.


Internationalfield course in manatee research techniques in dark waters using sonar, Costa Rica: Summary
of results and 1st announcement offuture course. On April 7-9, 2010 an international field course for research
techniques using sonar was held in Tortuguero, Costa Rica. The event was organized by the Costa Rican non-
government organization (NGO) Fundacion Trichechus, Submon (Spanish NGO based in Barcelona), and the
official Tortuguero Conservation Area (ACTo). Funding for the event was graciously provided by Barcelona
Zoo, Ajuntament of Barcelona, and Pachira/Evergreen Lodge located within Tortuguero. The primary
instructors were Dr. Leon Olivera-Gomez (Universidad Juarez Autonoma de Tabasco) and doctoral candidate
Daniel Gonzalez-Socoloske (Duke University), with contributions from Vet. Maria Luz Parga and Manel Gazo,
both of Submon. A total of 20 participants (see photo) attended the course from over 7 institutions representing
NGO's, government agencies, and academic institutions interested in manatee conservation in Costa Rica.
Representatives of all areas that contain manatees in Costa Rica were present including La Amistad Caribe
Conservation Area (ACLA-C), Wildlife Refuge Barra de Colorado (REBACO), and Tortuguero National Park
(PNT), as well as several students from the National University of Costa Rica. The field course was designed to
be as hands-on as possible and consisted of a combination of presentations in the mornings and field training
with the equipment in the evenings and nights. Participants were instructed on proper use and care of sonar
equipment (see Gonzalez-Socoloske et al., 2009). In addition, instruction was provided on how to collect
samples from dead manatees for genetic analysis. A presentation was given by Eduardo Chamorro, director of
PNT, stressing the current needs of the park in terms of manatee research. As a by-product of the course, a
research team consisting of members of Foundation Trichechus and ACTo was established to implement the use
of this methodology in a pilot study within PNT. Preliminary results from this two-month study indicate that
manatees were detected successfully with sonar in two locations within PNT. The research team is currently
analyzing the results of this pilot study to see if it can expand it to the other areas of known manatee presence in
Costa Rica. As an additional by-product of this course and pilot study, Fundacion Trichechus and ACTo teamed
up to participate in a cultural fair in Tortuguero on Sep 9-12 where they had a booth with information about
manatees. The sonar images of manatees from Tortuguero were a big hit among both children and adults and
sparked a renewed interest in the local people of Tortuguero, many of whom still doubted that they existed in
the area. For more information about this course, field study or the cultural fair contact Carlos Espinoza,
director of Fundacion Trichechus (c_espin@racsa.co.cr).
A similar course is currently being planned for April 2011 in Villahermosa, Mexico. It will focus on
methodologies using this technique and be as field-oriented as possible, taking advantage of the more than 20
resident manatees of Laguna de las Ilusiones in Villahermosa. For more information or if you are interested in
attending this field course please contact Dr. Leon Olivera Gomez (leon_olivera@yahoo.com.mx) or Daniel
Gonzalez-Socolokse (dg52@duke.edu)

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Gonzalez-Socoloske D., L. D. Olivera-Gomez, and R. E. Ford. 2009. Detection of free-ranging West Indian manatees Trichechus
manatus using side-scan sonar. Endangered Species Research 8:249-257.

Field course participants, Costa Rica.


Conservation Actions ofAmazonian Manatee (Trichechus inunguis) in Perui. The Amazonian manatee
(Trichechus inunguis) inhabits the Amazon River and its tributaries in Peru. It is currently considered a
vulnerable species in the IUCN and is legally protected by the Peruvian government. However, despite efforts
to protect and conserve, their populations are still declining mainly due to anthropogenic factors, particularly
indiscriminate hunting and illegal trade as pets.
Faced with this problem, efforts to rescue and rehabilitate the Amazonian manatee were initiated in 2007
in the department of Loreto, through the Gobierno Regional de Loreto, the Asociaci6n para la Conservaci6n de
la Biodiversidad Amaz6nica Dallas World Aquarium Zoo, The Dallas World Aquarium and the Instituto de
Investigaciones de la Amazonia Peruana. These groups have formed the Foundation Iquitos Amazon Rescue
Centre, which aims to provide institutional support for the rescue and rehabilitation of specimens of aquatic
mammals and endangered wildlife in Loreto, secured through a program of environmental education.
Thus, through suitable protocols 15 animals have been successfully rehabilitated, including 9 calves.
This work is complemented with an environmental education program for 2009 which sensitized about 40,000
people, mainly children and young people, in educational institutions in the city of Iquitos and Amazon villages
The group has also worked with management for the conservation laws of this species and we intend to
develop in the short term, with the support of ONGs and government institutions, a Plan of Action for the
conservation of river dolphins and manatees in the Peruvian Amazon.

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The Amazon Rescue Centre currently continues the task of rehabilitation of manatees, beginning with
the release of individuals rehabilitated in the "El Dorado" lagoon located in Yanayacu Pucate River in Samiria
Pacaya National Reserve. -Carlos M. Perea-Sicchar Luis J. VelAsquez-Varela2, Maribel Espinoza-Azan2,
Juan SAnchez Babilonia2, Daryl L. Richardson3 and Tulio C. Correa-Gir6n' (1Direcci6n Regional de la
Producci6n de Loreto, Ramirez Hurtado N0 645, Iquitos, Peru, www.acobia-dwazoo.org,
maici_perea@yahoo.com; 2Asociaci6n para la Conservaci6n de la Biodiversidad Amaz6nica Dallas World
Aquarium Zoo (ACOBIA-DWAZOO), Jose Galvez N0 1509, Iquitos, Peri; 3The Dallas World Aquarium, 1801
N. Griffin St., Dallas, Texas 75202 USA)


Manatees in Alabama waters: Sighting network and research update. The West Indian manatee,
indigenous to Florida (FL) in the United States, is a common visitor to the northern Gulf of Mexico, including
coastal Alabama (AL). Researchers at the Dauphin Island Sea Lab have been studying manatees in AL since
2007, when the Mobile Manatees Sighting Network (MMSN) was founded to receive and track manatee
sightings in AL waters. MMSN's 2010 research highlights include necropsy of a Tampa Bay manatee that
washed ashore in Orange Beach, AL during the exceptionally cold winter, ongoing reconnaissance related to the
Deepwater Horizon oil spill, capture and tagging of three additional manatees in Mobile Bay, regular
monitoring of four manatees tagged in AL, and the placement of passive acoustic monitors (PAMs) to detect
any belted manatees moving in AL.

Manatee necropsy in Orange Beach, AL
In January 2010, an adult male manatee was reported washed ashore in a residential area in Arnica Bay
on the Intracoastal Waterway in AL. MMSN responded and performed a necropsy in collaboration with the
Florida Fish and Wildlife Conservation Commission (FWC), which determined probable cause of death was
cold stress (one of many for the season). The manatee was photographed and identified in the MIPS system
(USGS Sirenia Project) as known from Tampa Bay, FL. Although this was the only known manatee mortality
in AL last winter, at least two other manatees were reported in AL waters during the period of extreme cold.
One manatee is believed to have succumbed to cold stress in FL, just east of the AL border. The fate of the
other animal is unknown.

Manatee captures and tagging in Alabama waters
During August 2010, MMSN researchers collaborated with Sea to Shore Alliance, Sea World Orlando,
and the University of FL to capture and tag three manatees in Mobile Bay. Located by aerial search, two
animals were captured in Dog River, and one was captured in the Mobile-Tensaw River Delta. All three
manatees were males in good condition, and all were tagged with GPS satellite telemetry tags. All three tagged
manatees remain in northern Mobile Bay and the Delta, feeding on aquatic vegetation such as Vallisneria,
Najas, and Myriophyllum, which are abundant in the area. By tracking and monitoring these animals, MMSN is
collecting data on behavior, habitat use, and movement patterns within Alabama, as well as large-scale seasonal
migration timing and direction.
MMSN has also continued monitoring two manatees tagged in Alabama in 2009 ("Bumpy" and
"Bama"). These two manatees traveled from AL to the Crystal River, FL area in fall 2009 and departed those
wintering grounds in late spring 2010. Both manatees resided in Apalachicola, FL for most of summer 2010
before Bama lost her tag (July) and Bumpy briefly returned to AL (late September). While in Apalachicola,
Bumpy was frequently found in proximity to manatees tagged by the USGS Sirenia Project in FL.

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Passive acoustic monitoring in Alabama
MMSN is currently deploying four PAMs in strategic locations throughout AL waters, including points
of entry or exit from Mobile Bay and favored habitat sites. These PAMs will record the presence of belted
manatees (animals previously tagged elsewhere but retaining some of the gear) in local waters. The monitors
will record data from any belt-mounted sonic transmitter, regardless of where the manatee was tagged. MMSN
personnel have observed at least three belted animals in AL waters in the past thirteen months. Using the PAMs
will quantitatively confirm and track movement of these and other known manatees through AL waters and
expand knowledge of their migrations.

Deepwater Horizon response in Alabama
Immediately after the Deepwater Horizon oil spill in April 2010, MMSN collaborated with other marine
mammal researchers to identify manatees and other large aquatic species potentially in danger or injured from
the spill. We continue these collaborative monitoring efforts, including monitoring tagged manatees as they
make their regular seasonal migration out of Mobile Bay and surrounding waters to warmer wintering grounds.
-Allen Aven and Ruth Carmichael (Dauphin Island Sea Lab, Dauphin Island, Alabama; The University of
South Alabama, Mobile, AL)

One manatee captured in Dog River in August 2010 sports his new accessories belt, tether, and GPS
tag. Photo credit: JoAnn Mitchell

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-_ -.~ - ---

Tagged manatee "Bama" checks out the MMSN researchers in Apalachicola, FL, in May 2010. Photo
credit: Katie Interlichia


Aragones, L. V., M. A. Roque, M. B. Flores, R. P. Encomienda, G. E. Laule, and B.G. Espinos. 2010. The
Philippine marine mammal strandings from 1998 to 2009: Animals in the Philippines in peril? Aquatic
Mammals, 36(3), 219-233.

A well-maintained marine mammal stranding database can be an invaluable tool in understanding not
only strandings but also changes in the marine environment. This study aimed to examine the following aspects
of marine mammal strandings in the Philippines: species composition, temporal (i.e., frequency of stranding per
year and seasonality) and spatial (i.e., frequency of stranding per region and province) variation, proportions of
alive or dead specimens, and stranding hotspots. In 2008, a systematic collection of data on strandings,
including out-of-habitat incidents, resulted in an initial 12-year database-from 1998 to 2009. A total of 178
stranding events were recorded: 163 single, 10 mass, and 5 out-of-habitat strandings, with an average of 15
observed stranding events annually. Twenty-three of the 28 confirmed species of marine mammals in the
Philippines were recorded to strand, including first-recorded specimens for the Indo-Pacific bottlenose dolphin
(Tursiops aduncus), pygmy sperm whale (Kogia breviceps), and Longman's beaked whale (Indopacetus
pacificus). The top five most frequent species to strand included spinner dolphin (Stenella longirostris) (n = 26),
short-finned pilot whale (Globicephala macrorhynchus) (n = 14), melon-headed whale (Peponocephala
electra) (n = 13), Risso's dolphin (Grampus griseus) (n = 11), and common bottlenose dolphin (T.
truncatus) (n = 10). Dugongs (Dugong dugon) stranded seven times since 2001. Strandings occurred throughout
the year with frequency significantly peaking during the northeast (NE) monsoon (November to March) season.
Overall, Regions III (Central Luzon) and VII (Central Visayas) had the highest number of strandings (both n =
27) followed by Regions I (Ilocos) (n = 22) and V (Bicol) (n = 18). The following provinces or local
government units were considered hotspots based on high number of strandings observed at each area:
w -..- -

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Zambales, Cagayan, Zamboanga City, Negros Oriental, Bohol, Pangasinan, and Bataan. Sixty-five percent of
all documented stranding events involved live (n = 116) animals. This high percentage might be linked to
dynamite fishing (causing acoustic trauma), fisheries interactions, or biotoxins from harmful algal blooms
coupled to their foodweb. These standings in general validate the diverse marine mammal assemblage in the
Philippines and reveal the various environmental threats with which they deal.

Beatty, B. L. and J. Geisler. in press. A stratigraphically precise record of Protosiren (Protosirenidae,
Sirenia) from North America. Neues Jahrbuch fur Geologie und Palaontologie Abhandlungen 257(4).
http://www.ingentaconnect.com/content/schweiz/njbgeol/pre-prints/0095 DOI: 10.1127/0077-7749/2010/0095

A partial left innominate of a sirenian, mostly consisting of the ilium, was recently recovered from the
late Middle Eocene (Bartonian) Cross Member of the Tupelo Bay Formation in Orangeburg County, South
Carolina. It most closely resembles the innominate of Protosiren sattaensis GINGERICH et al., 1995 from the
Bartonian of Pakistan, though due to the present lack of knowledge of variation within the genus, it is best
assigned to Protosiren sp. This specimen was collected from the same horizon as the holotype of Carolinacetus
gingerichi, representing an unusual case of Protosirenid and protocetid co-occurrence. This new material is the
first Eocene sirenian material diagnosable to the genus level that came from unambiguous, age-restricted strata
in North America. Previous reports of Eocene Sirenia from South Carolina have consisted of indeterminate rib
fragments and a skullcap described by Sanders, all from approximately Priabonian strata: the Pregnall Member
of the Cross Formation or the Harleyville Formation. Recent geologic studies of the Castle Hayne Formation
suggest that "Lutetian" Protosiren and dugongid material from North Carolina is instead Bartonian or
Priabonian in age. Thus after presumably dispersing westward from North Africa, prorastomid sirenians in the
Western Hemisphere first appear in Jamaica, Protosirenids and/or dugongids on the Gulf Coast, and then
Protosirenids and dugongids later in the Carolinas. The Bartonian marks the beginning of the Middle Eocene
Climatic Optimum, and this event may have aided the northward movement of sirenians in the Eocene.

Presented at the Society of Vertebrate Paleontology meeting, October 1 th, 2010, Pittsburgh, PA:
Dental microwear of modern and fossil sirenia reflects changes in the physical environment in the
neogene of Florida.
Beatty, Brian Lee, Dept. Anatomy, New York College of Osteopathic Medicine, Northern Boulevard, Old
Westbury, NY 11568
Mihlbachler, Matthew C., Dept. Anatomy, New York College of OIe'Ipq1thiic Medicine, Northern Boulevard,
Old Westbury, NY 11568

Manatees and dugongs are restricted to rivers and coastal habitats, feeding on plants usually bound to a
substrate. Peninsular Florida has changed much over time, including a change from carbonate to siliclastic
substrates during the Miocene and the emergence of a manatee-dominated ecosystem replacing a dugong-
dominated one. This shift is presumably connected, reflecting the specialization of manatee horizontal tooth
development as competitively advantageous in dealing with an increased source of abrasives over the primitive
tooth replacement found in dugongs. To test this, we looked at dental microwear of all subspecies of modem
and fossil Trichechus and compared them with Clarendonian and Hemphillian Metaxytheriumfloridanum, as
well as Crenatosiren and a possible Eocene Protosiren for added insight. Using digital photomicrographs taken
at 100x, pits and scratches were traced and partitioned into discrete size categories based on widths and
diameters, and counted in a 1.6x105lm2 square area, all by a single observer. Though the location on which
teeth were sampled had a marginal effect on the data, ANOVA results indicate that all populations, including
comparisons to modern aquarium-housed individuals, were significantly different for all features except for
very wide scratches (>20 [m width) and very wide pits (>50 [m width). Curiously, T manatus had more

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scratches than T. inunguis, suggesting that microwear features in marine herbivores are less likely a reflection of
wear by phytoliths and more likely wear by siliclastic substrate exposure. Rancholabrean T. m. bakerorum
appear to have had fewer scratches and Irvingtonian T. manatus even fewer, but with more pits. Clarendonian
Metaxytherium appear to have had many pits and scratches, compared to Hemphillian Metaxytherium which
had similar numbers of pits, but fewer scratches. More data is needed to determine what the causes of dental
microwear is for aquatic herbivores, yet our data suggests that microwear reflects measurable changes in
feeding ecology, whether it be substrate or dietary composition, experienced by Metaxytherium from the Middle
to Late Miocene and Trichechus throughout the Pleistocene.

Castelblanco-Martinez D. N., B. Morales-Vela, H. A. Hernandez-Arana, J. Padilla-Saldivar. 2009. Diet of
manatees Trichechus manatus manatus in Chetumal Bay, Mexico. Latin American Journal of Aquatic
Mammals 7:39-46.

Manatees, as well as other sirenians, are aquatic, opportunistic herbivores. Knowledge of their diet is
important to determine habitat requirements. This is the first study of manatee diet in Mexico. Our main
objective was to identify the plant species eaten by manatees in Chetumal Bay, and to establish if diet
composition varied by climatic season, sex or age class. We compared plant epidermal fragments found in
digestive contents with histological descriptions and permanent collections of suspected plants and algae.
Thirty-six fecal samples and nine tract digestive content samples (mouth, stomach, and cecum) were examined.
We found eight distinct plant items, including seagrasses, freshwater grasses, algae and vascular plants.
Halodule wrightii and Thalassia testudinum were found in 41 samples (92%), and Ruppia sp. was present in
57.8%. Another common item was red mangrove (Rhizophora mangle), found in 66.7% of samples.
Additionally, we report Chara sp. and Najas sp. as part of the West Indian manatee's diet outside of Florida. A
multivariate analysis based on a presence/absence triangular matrix and a similarity analysis were used to test
differences among samples. Season, sex or age class did not influence diet composition. All species identified
are present in Chetumal Bay, suggesting that manatees do not move long distances at sea in search of food. We
postulate that consumption of red mangrove by Chetumal Bay manatees may occur as compensation for the
scarcity of submersed aquatic plants.

J. Denkinger. 2010. Status of the Amazonian manatee (Trichechus inunguis) in the Cuyabeno Reserve,
Ecuador. Avances, Vol. 2, pp. B29-B34.

Amazonian manatees live in black water rivers and lakes in the Amazon basin. A study of Amazonian
manatees in the Cuyabeno Reserve conducted by Timm et al. [1] in 1983 gave the first information on
distribution of manatees in the Cuyabeno Reserve and they suggested a possible extinction of the Amazonian
Manatee in the following decade. Here I present results of observations and interviews realized 13 years after
the first study as complementary observations during a research project on Amazon River dolphins (Inia
geoffrensis) from 1996 to 1999. We surveyed during more than 127 days covering about 6.175km in manatee
habitat with more than 456 hours continuously observing black water rivers and lagoons and we carried out
manatee surveys paddling in the Lagunas Grandes de Cuyabeno. Interviews with tour guides, park rangers and
native Indians give a complete sighting list for the presence of manatees and insight into the current situation in
the Reserve.
The relative abundance of manatees in the Cuyabeno River is 0.01 animals/h effort and even less in the
Lagartococha River with 0.007 animals/h effort. Populations in the Lagartococha River seem to be severely
reduced. Hunting in both rivers continued despite legal protection with 16 manatees killed from 1995 to 1998.
Overall 40 to 49 animals were seen in the Cuyabeno Reserve from 1996 to 1998. Even though, predictions that
manatees would be extinct by 1993 were not fulfilled, they are rare in the Reserve and living in a protected area

Sire~ews No. 54

October 20100

does not necessarily safeguard this species.
Keywords:. Amazonian manatee, Trichechus inunguis, status, Cuyabeno Reserve, Ecuador.


Astibia, H., N. Bardet, X. Pereda-Suberbiola, A. Payros, V. de Buffrenil, J. Elzora, J. Tosquella, A. Berreteaga,
and A. Badiola. 2010. New fossils of Sirenia from the Middle Eocene of Navarre (Western
Pyrenees): The oldest West European sea cow record. Geological Magazine 147(5):665-673.

Buffrenil, V. de, A. Canoville, R. D'Anastasio, and D. P. Domning. 2010. Evolution of sirenian
pachyosteosclerosis, a model-case for the study of bone structure in aquatic tetrapods. Journal of Mammalian
Evolution 17: 101-120.
Domning, D. P., I. S. Zalmout, and P. D. Gingerich. 2010. Sirenia. Chap. 14 in: L. Werdelin & W. J. Sanders
(eds.), Cenozoic Mammals of Africa. Berkeley: University of California Press: 147-160.
Henaut, Y., S. P. Becerra Lopez, S. Machkour-M'Rabet, B. Morales-Vela, P. Winterton, and F. Delfour. 2010.
Activities and social interactions in captive Antillean manatees in Mexico. Mammalia 74(2):141-146.

Jett, J. S., and B. Thapa. 2010. Manatee zone compliance among boaters in Florida. Coastal Management

Lanyon, J. M., H. L. Sneath, and T. Long. 2010. Three skin sampling methods for molecular characterisation of
free-ranging Dugong (Dugong dugon) populations. Aquatic Mammals, 36(3), 298-306.

Pabody, C. M., R. Carmichael, L. Rice, and M. Ross. 2009. A new sighting network adds to 20 years of
historical data on fringe West Indian (Trichechus manatus) manatee populations in Alabama waters. Gulf of
Mexico Science, 2009(1), pp. 52-61.

Pantoja, T. M. A., F. C. W. Rosas, V. M. F. da Silva, and A. M. F. dos Santos. 2010. Urinary parameters of
Trichechus inunguis (Mammalia, Sirenia): Reference values for the Amazonian manatee. Brazilian Journal of
Biology 70(3):607-615.

Suarez-Morales, E., B. Morales-Vela, J. Padilla-Saldivar, and M. Silva-Briano. 2010. The copepod
Balaenophilus manatorum (Ortiz, Lalana and Torres, 1992) (Harpacticoida), an epibiont of the Caribbean
manatee. Journal of Natural History 44(13-14):847-859. 2010.

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