Savu Sea and Surrounding Areas IMMA

Size in Square Kilometres

160 512 km2

Qualifying Species and Criteria

Sperm whale – Physeter macrocephalus

Criterion A; B (2); C (1)

Spinner dolphin – Stenella longirostris

Criterion B (1); C (1, 2)

Melon-headed whale – Peponocephala electra

Criterion B (1)

Fraser’s dolphin – Lagenodelphis hosei

Criterion B (1)

Pygmy blue whale – Balaenoptera musculus brevicauda

Criterion A; B (2); C (2, 3)

Indo-Pacific bottlenose dolphin – Tursiops aduncus

Criterion B (1)

Marine Mammal Diversity 

Criterion D (2)

Physeter macrocephalus, Stenella longirostris, Stenella attenuata, Peponocephala electra, Grampus griseus, Lagenodelphis hosei, Feresa attenuata, Balaenoptera musculus brevicauda, Tursiops aduncus, Kogia sima, Kogia breviceps, Globicephala macrorhynchus, Orcinus orca, Pseudorca crassidens, Steno bredanensis, Ziphius cavirostris, Balaenoptera edeni, Balaenoptera musculus, Megaptera novaeangliae, Tursiops truncatus, Dugong dugon

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The Savu Sea and surrounding areas in the East Nusa Tenggara Province is an important area for marine mammals in Indonesia. The area provides critical habitat for these species, such as migratory corridors, feeding and nursery areas. The area supports a wider diversity of 22 species of marine mammal including vulnerable and endangered species such as Blue Whale and Sperm Whale. Ombai Strait and the Timor Sea are also contained within the IMMA boundary and have been identified as a migratory corridor for the Pygmy Blue Whale. This corridor in the Savu Sea connects the migratory line between north-west Australia and Banda-Seram Seas. All marine mammals in Indonesia have been fully protected since 1999 and this area was declared as the Savu Sea Marine National Park, of which one of their roles in the protection of marine mammals. However, traditional whaling communities are still identified as a threat to the cetacean population within the region, as well as illegal, unreported and unregulated fishing, increasing marine traffic, and oil-gas exploration.

Description of Qualifying Criteria

Criterion A – Species or Population Vulnerability

Blue whales (Balaenoptera musculus) was confirmed to be found across the Savu and Timor Seas, and has been assessed by the IUCN Red List as an Endangered species (Dethmers et al. 2009). In addition, the presence of the pygmy blue whale (Balaenoptera musculus brevicauda) have also been confirmed to use this region as a migration corridor (Double et al. 2014). However, the current status of pygmy blue whale is very uncertain with a listing as Data Deficient on the Red List of Threatened Species. Nevertheless, it is possible that commercial and small scale whaling has caused a decrease in the number of pygmy blue whales, with their recovery being slower than the Antarctic blue whale (Branch et al. 2007; Branch et al. 2009). In the 2013 boat-based survey, blue whales were recorded in 5 separate sightings from the Savu Islands to NW Timor (Kahn and Fajariyanto, 2014). In 2008 aerial and boat based surveys of Timor Leste waters observed blue whales, with two adults sighted in September and a group of two adults with a calf sighted in November in the north-western coastal waters offshore from the Dili and Liquisa districts (Dethmers et al. 2009). Field surveys in Solor waters during May-October 2017 also recorded 5 sightings of pygmy blue whale, including 7 individuals; pygmy blue whales were further reported in October 2017 in Waihenga Bay-Lembata (Putra et al. 2017). Double and colleagues further tracked 11 pygmy blue whales from Australia in April 2011, 5 individual of which were successfully tracked and entered Savu Sea waters in June 2011 and spend several days to pass this area before they moved into the Banda Sea and Moluccas Sea (Double et al. 2014). Sperm whales (Physeter macrocephalus) have been assessed by the IUCN as a Vulnerable species. However, In Indonesia the hunters of Lamalera in the Savu Sea region have hunted sperm whales for more than 500 years, and drives haves declined 80% in catch rates of sperm whale in Solor waters of the Savu Sea, that indicate a potential wider decrease of their population in this region (Mustika, 2006).

Criterion B: Distribution and Abundance

Sub-criterion B1: Small and Resident Populations

The Alor Strait (Between Lembata and Pantar), in particular the area near Marisa Island which is located in the middle of a main migratory corridor (and shipping lane), also inhabited by residential pods of spinner dolphin (Kahn and Hennicke, 2017). Survey results also indicates several areas with resident small cetaceans i.e. hundreds of Spinner dolphin in Barate bay which can be observed every morning and afternoon in this bay (Kahn and Fajariyanto, 2014). Pantar Strait (between Pantar and Alor), in particular the area around Pura Island, is inhabited by a residential pod of mixed cetaceans including Melon-headed whales,  Fraser’s dolphins, and  Spinner dolphins. This mixed pod has been stable in group-composition and has been consistently sighted in this area for at least 4 years (Kahn, 2005; Kahn and Fajariyanto, 2014). Indo-pacific bottlenose dolphin Tursiops aduncus has been assessed as Data Deficient by IUCN Red List. A small pod of Indo-pacific bottlenose can be consistently observed Kalabahi Bay with only 3-6 individuals, while a further 6 individuals were also observed in the straits between Pantar and Lembata Island (Kahn and Hennicke, 2017). Furthermore, the Spinner dolphin is the most frequently observed species in Solor waters of the Savu Sea (Putra and Topan, Forthcoming). While, long-term rapid ecological assessment (REA) of the oceanic cetacean program in 2001-2005, also recorded that the Spinner dolphin is relatively consistent as the most abundant species in this region (Kahn, 2002; Kahn, 2004a; Kahn, 2004b; Kahn 2005). The Spinner dolphin that can be found year-round in this region and is likely to be a resident species.

Sub-criterion B2: Aggregations

Based upon the year-round monitoring program in Solor Waters off Savu Sea, the seasonal aggregations of Oceanic dolphins peak in the relative abundance during June to November, although they also can be found in the early of the year (Putra and Topan, forthcoming). The seasonal aggregation of these species increases during June to November in this region, and is strongly related to the oceanographic features (i.e. upwelling current, mesoscale eddies, and thermal and chlorophyll-a front) that provide high primary productivity  (Adriani, 2010). The upwelling current that associated with eddies and internal waves in this region has increased the local productivity. The pygmy blue whale annually migrates through the area from Western Australia to the Banda Sea through the Savu Sea, and is strongly-associated with upwelling period in Eastern Indonesia (Double et al. 2014). One bull sperm whales (estimated length 18m) was sighted in 2013 from a survey North of Timor Island waters (Kahn and Fajariyanto, 2014). Male sperm whale were seen on two occasions on the 2015 boat-based survey, as well as identified acoustically at several listening stations (Kahn and Hennicke, 2017). Many social behaviours as well as breaches were observed at close proximity to the boat. This group was tracked acoustically and visually and close observations were made continually over 5 hours.
Furthermore, recent study from Putra and Topan (Forthcoming) found the inter-annual variation on their aggregations was influenced by ENSO, where the oceanic dolphin relative abundance increased during positive El Niño, while the relative abundance of whales was decreased.

Criterion C: Key Life Cycle Activities

Sub-criterion C1: Reproductive Areas

Young oceanic dolphins and calves (i.e. Spinner dolphin, Pantropical dolphin, Fraser’s dolphin etc.) have been recorded frequently in Solor Waters, where they was seen together in the big pods with adult dolphins (Putra et al. 2017). Solor waters are potentially used as a nursery ground for these dolphin species. Furthermore, Kahn and Colleagues also observed a 3 meter Humpback whale mother and calf pair in the South of Sabu Island, and calves of Spinner dolphins in Southwest of Tuakau Cape, Timor Island (Kahn and Fajariyanto, 2014). While, in 2015 they also recorded both young Spinner dolphins and Sperm whales in the south of east Pantar Island, South of Lembata, and West part of Pantar Island (Kahn and Hennicke 2017).

Sub-criterion C2: Feeding Areas

The presence of important oceanographic features in this region (e.g. upwelling current, bathymetry slope, thermal front and mesoscale eddies) support high-densities of prey species. Studies have found that cetacean aggregate closely to frontal zones and eddies, which provide a high-density of prey for oceanic dolphins and whales; where their distribution was described in the areas of productivity hotspot (Putra et al. 2016), as well close to the transition zone of fronts and eddies that indicate their foraging (Adriani, 2010). In Solor waters, local fishermen also report that the spinner dolphins often interact with their fishery activity (e.g. gillnet and purse seine) during night hours, where they swim actively to access to mesopelagic prey, sometimes becoming trapped in the fisher’s nets (Putra et al. 2017). During some sightings pods of dolphins were associated with seabird aggregations, indicating further feeding/foraging behaviour in this area (MIH Putra personal observation). Furthermore, the several studies of Pygmy blue whale describe that the movement pattern of this species is strongly associated with the dynamic of local productivity that occurs inthge Savu Sea, where the Pygmy blue whale is likely utilizing this region for feeding (Kahn, 2005; Double et al. 2014).

Sub-criterion C3: Migration Areas

The Savu Sea appears to provide a critical migratory habitat for certain marine mammal species. Based on the tagging studies of Double and Colleagues (2014), the Ombai Strait and Timor Sea has been observed to function as a migration corridor for pygmy blue whales, which migrate from Western Australia to Eastern Indonesia Sea (Sunda-Banda-Halmahera ecoregion). This species was recorded arriving in the Savu Sea in the end of May, continuing their migration to the Banda Seram Sea through Solor-Alor waters, the Timor Sea, and Ombai Strait.

Criterion D: Special Attributes

Sub-criterion D2: Diversity

The Savu Sea and Surrounding Areas IMMA provides a habitat for at least 22 recorded species of marine mammal, which includes beaked whales, blue whale, Bryde’s whale, common bottlenose dolphin, Cuvier’s beaked whale, dugong, dwarf sperm whale, false killer whale, Fraser’s dolphin, humpback whale, Indo-Pacific bottlenose dolphin, melon-headed whale, orca, pantropical spotted dolphin, pygmy blue whale, pygmy killer whale, pygmy sperm whale, risso’s dolphin, rough-toothed dolphin, short-finned pilot whale, sperm whale, and spinner dolphin (Kahn, 2005; Kahn and Fajariyanto, 2014; Kahn and Hennicke, 2017; Putra et al. 2017).

Supporting Information

Adriani. 2010. Cetacean community and habitat characteristics in the Ombai Strait. Master thesis. Bogor Agricultural University.

Branch, T.A., Abubaker, E.M.N., Mkango, S. and Butterworth, D.S. 2007. Separating southern blue whale subspecies based on length frequencies of sexually mature females. Marine Mammal Science, 23(4), pp.803-833.

Branch, T.A., Mikhalev, Y.A. and Kato, H. 2009. Separating pygmy and Antarctic blue whales using long‐forgotten ovarian data. Marine Mammal Science, 25(4), pp.833-854.

Dethmers, K., Chatto, R., Meekan, M., Amaral, A., de Cunha, C., de Carvalho, N. and Edyvane, K. 2009. Marine megafauna surveys in Timor Leste: identifying opportunities for potential ecotourism – Final Report. Ministry of Agriculture & Fisheries, Government of Timor Leste.

Double, M.C., Andrews-Goff, V., Jenner, K.C.S., Jenner, M.N., Laverick, S.M., Branch, T.A. and Gales, N.J., 2014. Migratory movements of pygmy blue whales (Balaenoptera musculus brevicauda) between Australia and Indonesia as revealed by satellite telemetry. PLoS One, 9(4), p.e93578.

Kahn, B. and Fajariyanto, Y. 2014. Rapid Ecological Assessment (REA) for Cetaceans in the Savu Sea Marine National Park. The Nature Conservancy – Indonesia Coasts and Oceans Program.

Kahn, B. and Hennicke, J. 2017. A Business Plan for Responsible and Sustainable Whale Watching in the Alor Archipelago, Nusa Tenggara Timor (NTT), Indonesia: A best practice start-up guide for new whale watch operators and considerations for effective management of Indonesia’s cetacean tourism development. Technical Report for The Nature Conservancy – Indonesia Coasts and Oceans Program.

Kahn, B. 2000. Komodo National Park Cetacean Surveys-A rapid ecological assessment of cetacean diversity, abundance and distribution: April 2000. Interim Report to The Nature Conservancy Indonesia Coastal and Marine Program. 24pp.

Kahn, B. 2001. Komodo National Park Cetacean surveys. Technical Report prepared for TNC Indonesia Coasts and Oceans Program.

Kahn, B. 2002. Alor Rapid Ecological Assessment–Visual and acoustic cetacean surveys and evaluation of traditional whaling practices, fisheries interactions and nature-based tourism potential: October 2001 and May 2002 Survey Periods. Technical Report prepared for WWF-Wallacea and TNC Coastal and Marine Program Indonesia.

Kahn, B. 2004a. Solor-Alor visual and acoustic cetacean surveys: Interim report April–May 2003 survey period. Technical Report prepared for TNC Indonesia Coasts and Oceans Program.

Kahn, B. 2004b. Indonesia oceanic cetacean program activity report: October-December 2003 survey period. Technical Report prepared for TNC Indonesia Coasts and Oceans Program.

Kahn, B. 2005. Indonesia oceanic cetacean program activity report: April–June 2005. Technical Report prepared for TNC Indonesia Coasts and Oceans Program.

Kahn, B. and Vance-Borland, K., 2014. Marine Conservation Planning and the Offshore Oil & Gas and Deep-Sea Mining, and Shipping Industries in the Coral Triangle and South West Pacific: Large-Scale Spatial Analysis of the Overlap between Priority (p. 66). Technical Report prepared for WWF Australia.

Moore, T.S. and Marra, J., 2002. Satellite observations of bloom events in the Strait of Ombai: Relationships to monsoons and ENSO. Geochemistry, Geophysics, Geosystems, 3(2).????

Mustika, P.L.K. 2006. Marine mammals in the Savu Sea (Indonesia): indigenous knowledge, threat analysis and management options. Master thesis. James Cook University.

Putra, M.I.H., Lewis, S.A., Kurniasih, E.M., Prabuning, D. and Faiqoh, E. 2016, November. Plankton Biomass Models Based on GIS and Remote Sensing Technique for Predicting Marine Megafauna Hotspots in the Solor Waters. In IOP Conference Series: Earth and Environmental Science, Vol. 47, No. 1, p. 012015. IOP Publishing.

Putra, M.I.H., Topan E. and Lewis, S. 2017. Technical report Marine Megafauna in Solor Waters, East Flores – East Nusa Tenggara, Indonesia 2016 – 2017. Misool Foundation, Savu Sea Program, Indonesia. 61 pp.

Putra, M.I.H. and Topan, E. Forthcoming. Key environmental in driving the temporal trends of cetacean abundance in Solor waters off Savu Sea, Indonesia.

Putra, M.I.H. and Mustika, P.L.K. Forthcoming. Incorporating prey distribution into foraging habitat modelling for marine megafauna in the Savu Sea, Indonesia. Aquatic conservation: marine and freshwater ecosystems.

Sahri, A., Putra, M.I.H., Mustika, P.L.K., Kreb, D. and Murk, T. Forthcoming. Cetacean habitat suitability modelling in Indonesia: An effort to provide their more detailed distributions for conservation.


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