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Short-finned Pilot Whale

Globicephala macrorhynchus

2025 Red list status
Least Concern
Decline
Regional Population Trend
Increasing
Change compared
to 2016
No Change
Overview
Red list assessment
Regional Distribution and Occurrence
Climate change
Population information
Population genetics
Habitats and ecology
Use and Trade
Threats
Conservation
Bibliography

Overview

Globicephala macrorhynchus – Gray, 1846

ANIMALIA – CHORDATA – MAMMALIA – ARTIODACTYLA – DELPHINIDAE – Globicephala – macrorhynchus 

Common Names: Short-finned Pilot Whale, Pacific Pilot Whale (English), Kortvinloodswalvis (Afrikaans)  

Synonyms: Globicephala macrorhynchus Gray, 1846; Globicephala scammoni Bailey, 1936 

Taxonomic Note: 
Two morphological forms of Short-finned Pilot Whales (Globicephala macrorhynchus) are found off northern and southern Japan, differing in external and cranial morphology (Kasuya et al. 1988, Van Cise et al. 2016). Although it has been suggested that these might represent two distinct subspecies (Oremus et al. 2009), evidence has not been marshalled to make this distinction official and no subspecies of Short-finned Pilot Whale are currently recognised (Van Cise et al. 2016, Committee on Taxonomy 2024). 

Red List Status: LC – Least Concern, (IUCN version 3.1) 

Assessment Information

Assessors: Penry, G.,1James, B.S.2 & da Silva, J.3 

Reviewer: Purdon, J.4,5 

Institutions: 1Nelson Mandela University, 2The Centre for Statistics in Ecology, the Environment and Conservation, University of Cape Town, 3South African National Biodiversity Institute, 4TUT Nature Conservation, 5The Whale Unit, University of Pretoria 

Previous Assessors: Cockcroft, V. & Relton, C. 

Previous Reviewer: Plön, S. 

Previous Contributors: Atkins, S., Child, M.F., Elwen, S., Findlay, K., Meÿer, M. & Oosthuizen, H. 

Assessment Rationale 

Short-finned Pilot whales (Globicephala macrorhynchus) are widely distributed species across the globe, where their offshore distribution patterns may overlap with major increasing threats such as long-line fishing, shipping lanes, and seismic exploration activities in the assessment region. Although this species is unstudied in the assessment region, based on strandings and opportunistic sightings data, they appear to be relatively common offshore; and, in other parts of the world, increases in population size have been documented. While the general threats outlined for pelagic species could also apply here, there are no known threats that could cause a range-wide decline. However, there are no population size and trend data for the region of assessment and the taxonomy is uncertain, thus this species will need to be re-assessed as new data emerge. Additionally, as this species is deep-diving, it may be increasingly threatened by the emerging threats of underwater marine noise and plastic pollution, the effects of which should be monitored. Currently, Short-finned Pilot Whales are not conservation priorities within the assessment region as they are globally abundant (for example, 589,000 in the tropical Pacific). Therefore, they are listed as Least Concern.

Regional population effects: Pilot whales presumably occur seasonally in South African waters, and although continued research into their seasonal distribution and movements is required, no barriers to dispersal are recognised, thus rescue effects are considered possible. 

Reasons for Change 

Reason(s) for Change in Red List Category from the Previous Assessment: No change 

Red List Index 

Red List Index: No change 

Recommended citations: Penry G, James BS & da Silva JM. 2025. A conservation assessment of Globicephala macrorhynchus. In Patel T, Smith C, Roxburgh L, da Silva JM & Raimondo D, editors. The Red List of Mammals of South Africa, Eswatini and Lesotho. South African National Biodiversity Institute and Endangered Wildlife Trust, South Africa.

Regional Distribution and occurrence

Geographic Range

Short-finned Pilot whales are widely distributed with little geographic overlap in their range with Long-finned Pilot Whales (Gmelas). The Short-finned Pilot Whales occur in the warm tropics and subtropics, predominantly in deep offshore waters of the North Atlantic, the Pacific and the Indian oceans (Reilly & Shane 1986; Olson 2018), but also commonly occur in northern Angolan waters (Weir 2011, 2019) Within the southern African subregion, they have been recorded from Gabon, Angola, possibly Namibia, South Africa, Madagascar, Réunion, the Comoro Islands, and the Seychelles (Best 2007).

Within the assessment region, van Bree et al. (1978) indicated that Short-finned Pilot Whales are generally restricted to the east coast of South Africa. They presumably range from the east coast of South Africa, southwards to Cape St Francis, Eastern Cape (van Bree 1971), although strandings at Sedgefield, and a skull found near Mossel Bay suggest a slight extension to this westerly limit, most likely due to the southern extension of the warm Agulhas Current on the east coast of southern Africa (Best 2007;Skinner & Chimimba 2005). The most reliable westerly record of G. macrorhyncus off South Africa is from Jeffrey’s Bay (25 °E) (Ross, 1984). This species typically occurs in waters deeper than 1,000 m, beyond the edge of the continental shelf. 

Elevation / Depth / Depth Zones 

Elevation Lower Limit (in metres above sea level): (Not specified) 

Elevation Upper Limit (in metres above sea level): (Not specified) 

Depth Lower Limit (in metres below sea level): (Not specified) 

Depth Upper Limit (in metres below sea level): (Not specified) 

Depth Zone: (Not specified) 

Map

Figure 1. Distribution records for Short-finned Pilot Whale (Globicephala macrorhynchus) within the assessment region (South Africa, Eswatini and Lesotho). Note that distribution data is obtained from multiple sources and records have not all been individually verified.

Biogeographic Realms 

Biogeographic Realm: Afrotropical, Australasian, Indomalayan, Nearctic, Neotropical, Oceanian, Palearctic 

Occurrence 

Countries of Occurrence 

Country  Presence  Origin  Formerly Bred  Seasonality 
American Samoa  Extant  Native    Resident 
Angola  Extant  Native    Resident 
Anguilla  Extant  Native    Resident 
Antigua and Barbuda  Extant  Native    Resident 
Aruba  Extant  Native    Resident 
Australia  Extant  Native    Resident 
Bahamas  Extant  Native    Resident 
Bangladesh  Extant  Native    Resident 
Barbados  Extant  Native    Resident 
Belize  Extant  Native    Resident 
Benin  Extant  Native    Resident 
Bermuda  Extant  Native    Resident 
Bonaire, Sint Eustatius and Saba  Extant  Native    Resident 
Brazil  Extant  Native    Resident 
British Indian Ocean Territory  Presence Uncertain  Native    Seasonal Occurrence Uncertain 
Brunei Darussalam  Extant  Native    Resident 
Cabo Verde  Extant  Native    Resident 
Cambodia  Extant  Native    Resident 
Cameroon  Extant  Native    Resident 
Canada  Extant  Native    Resident 
Cayman Islands  Extant  Native    Resident 
Chile  Extant  Native    Resident 
China  Extant  Native    Resident 
Christmas Island  Presence Uncertain  Native    Seasonal Occurrence Uncertain 
Cocos (Keeling) Islands  Extant  Native    Resident 
Colombia  Extant  Native    Resident 
Comoros  Extant  Native    Resident 
Congo  Extant  Native    Resident 
Congo, The Democratic Republic of the  Extant  Native    Resident 
Cook Islands  Extant  Native    Resident 
Costa Rica  Extant  Native    Resident 
Cuba  Extant  Native    Resident 
Curaçao  Extant  Native    Resident 
Côte d’Ivoire  Extant  Native    Resident 
Djibouti  Extant  Native    Resident 
Dominica  Extant  Native    Resident 
Dominican Republic  Extant  Native    Resident 
Ecuador  Extant  Native    Resident 
El Salvador  Extant  Native    Resident 
Equatorial Guinea  Extant  Native    Resident 
Eritrea  Extant  Native    Resident 
Fiji  Extant  Native    Resident 
French Guiana  Extant  Native    Resident 
French Polynesia  Extant  Native    Resident 
Gabon  Extant  Native    Resident 
Gambia  Extant  Native    Resident 
Ghana  Extant  Native    Resident 
Grenada  Extant  Native    Resident 
Guadeloupe  Extant  Native    Resident 
Guam  Extant  Native    Resident 
Guatemala  Extant  Native    Resident 
Guinea  Extant  Native    Resident 
Guinea-Bissau  Extant  Native    Resident 
Guyana  Extant  Native    Resident 
Haiti  Extant  Native    Resident 
Honduras  Extant  Native    Resident 
Hong Kong  Presence Uncertain  Native    Seasonal Occurrence Uncertain 
India  Extant  Native    Resident 
Indonesia  Extant  Native    Resident 
Iran, Islamic Republic of  Extant  Native    Resident 
Jamaica  Extant  Native    Resident 
Japan  Extant  Native    Resident 
Kenya  Extant  Native    Resident 
Kiribati  Extant  Native    Resident 
Korea, Democratic People’s Republic of  Extant  Native    Resident 
Korea, Republic of  Extant  Native    Resident 
Liberia  Extant  Native    Resident 
Macao  Presence Uncertain  Native    Seasonal Occurrence Uncertain 
Madagascar  Extant  Native    Resident 
Malaysia  Extant  Native    Resident 
Malaysia -> Peninsular Malaysia  Extant  Native    Resident 
Malaysia -> Sabah  Extant  Native    Resident 
Malaysia -> Sarawak  Extant  Native    Resident 
Maldives  Extant  Native    Resident 
Marshall Islands  Extant  Native    Resident 
Martinique  Extant  Native    Resident 
Mauritania  Extant  Native    Resident 
Mauritius  Extant  Native    Resident 
Mayotte  Extant  Native    Resident 
Mexico  Extant  Native    Resident 
Micronesia, Federated States of  Extant  Native    Resident 
Montserrat  Presence Uncertain  Native    Seasonal Occurrence Uncertain 
Morocco  Extant  Native    Resident 
Mozambique  Extant  Native    Resident 
Myanmar  Extant  Native    Resident 
Namibia  Extant  Native    Resident 
Nauru  Extant  Native    Resident 
New Caledonia  Extant  Native    Resident 
New Zealand  Extant  Native    Resident 
Nicaragua  Extant  Native    Resident 
Nigeria  Extant  Native    Resident 
Niue  Extant  Native    Resident 
Norfolk Island  Presence Uncertain  Native    Seasonal Occurrence Uncertain 
Northern Mariana Islands  Extant  Native    Resident 
Oman  Extant  Native    Resident 
Pakistan  Extant  Native    Resident 
Palau  Extant  Native    Resident 
Panama  Extant  Native    Resident 
Papua New Guinea  Extant  Native    Resident 
Peru  Extant  Native    Resident 
Philippines  Extant  Native    Resident 
Pitcairn  Extant  Native    Resident 
Portugal  Extant  Native    Resident 
Puerto Rico  Extant  Native    Resident 
Russian Federation  Extant  Native    Resident 
Réunion  Extant  Native    Resident 
Saint Barthélemy  Extant  Native    Resident 
Saint Helena, Ascension and Tristan da Cunha  Extant  Native    Resident 
Saint Kitts and Nevis  Extant  Native    Resident 
Saint Lucia  Extant  Native    Resident 
Saint Martin (French part)  Extant  Native    Resident 
Saint Vincent and the Grenadines  Extant  Native    Resident 
Samoa  Extant  Native    Resident 
Sao Tome and Principe  Extant  Native    Resident 
Saudi Arabia  Extant  Native    Resident 
Senegal  Extant  Native    Resident 
Seychelles  Extant  Native    Resident 
Sierra Leone  Extant  Native    Resident 
Singapore  Extant  Native    Resident 
Sint Maarten (Dutch part)  Extant  Native    Resident 
Solomon Islands  Extant  Native    Resident 
Somalia  Extant  Native    Resident 
South Africa  Extant  Native    Resident 
Spain  Extant  Native    Resident 
Sri Lanka  Extant  Native    Resident 
Suriname  Extant  Native    Resident 
Taiwan, Province of China  Extant  Native    Resident 
Tanzania, United Republic of  Extant  Native    Resident 
Thailand  Extant  Native    Resident 
Timor-Leste  Presence Uncertain  Native    Seasonal Occurrence Uncertain 
Togo  Extant  Native    Resident 
Tokelau  Presence Uncertain  Native    Seasonal Occurrence Uncertain 
Tonga  Extant  Native    Resident 
Trinidad and Tobago  Extant  Native    Resident 
Turks and Caicos Islands  Extant  Native    Resident 
Tuvalu  Extant  Native    Resident 
United States of America  Extant  Native    Resident 
Uruguay  Presence Uncertain  Native    Seasonal Occurrence Uncertain 
Vanuatu  Extant  Native    Resident 
Venezuela, Bolivarian Republic of  Extant  Native    Resident 
Viet Nam  Extant  Native    Resident 
Virgin Islands, British  Extant  Native    Resident 
Virgin Islands, U.S.  Extant  Native    Resident 
Wallis and Futuna  Extant  Native    Resident 
Western Sahara  Extant  Native    Resident 
Yemen  Extant  Native    Resident 

Large Marine Ecosystems (LME) Occurrence 

Large Marine Ecosystems: (Agulhas Somali Current Large Marine Ecosystem (ASCLME); Benguela Current Large Marine Ecosystem (BCLME)) 

FAO Area Occurrence 

  Presence  Origin  Formerly Bred  Seasonality 
21. Atlantic – northwest  Extant  Native     
27. Atlantic – northeast  Extant  Native     
31. Atlantic – western central  Extant  Native     
34. Atlantic – eastern central  Extant  Native     
37. Mediterranean and Black Sea  Extant  Native     
41. Atlantic – southwest  Extant  Native     
47. Atlantic – southeast  Extant  Native     
51. Indian Ocean – western  Extant  Native     
57. Indian Ocean – eastern  Extant  Native     
61. Pacific – northwest  Extant  Native     
67. Pacific – northeast  Extant  Native     
71. Pacific – western central  Extant  Native     
77. Pacific – eastern central  Extant  Native     
81. Pacific – southwest  Extant  Native     
87. Pacific – southeast  Extant  Native     

Climate change

Although the impacts of climate change to Pilot Whales are largely unknown, it is likely that changes in water temperature and CO2 concentration will have cascading effects on Pilot Whale movements and feeding ecology. Learmonth et al. (2006) reported that in the Faroe Islands, where Long-finned Pilot Whales have been historically hunted, catch rates were positively correlated with occurrence of a popular prey species, Todarodes sagittatus. This pelagic squid is thought to be either directly influenced by water temperature and CO2 concentration, or possibly indirectly influenced by productivity (Bjørge 2002). Short-finned Pilot Whales are likely to be similarly affected. Additionally, environmental variation as a result of the 1982–1983 El Niño is likely to have indirectly caused the absence of Short-finned Pilot Whales, and their associated prey-species Loligo opalescens, in some regions. 

Cetacean morbillivirus was responsible for the deaths of at least 60 Long-finned Pilot Whales in the Mediterranean (Bellière et al. 2011) with surviving individuals often exhibiting decreased long-term survival due to chronic infections and immunosuppression (Pons et al. 2022). Short-finned Pilot Whales have also been found to contract Cetacean morbillivirus (a family of approximately 30 viruses that affect marine mammals) and at least four individuals stranded off Brazil between July and October 2020 were positive for one of these viruses (Cost-Silva et al. 2023). Such incidents are likely to become more prevalent as the impacts of climate change, especially increasing sea surface temperatures (Sanderson and Alexander, 2020), and ship-avoidance behaviour increase, which may force both species into environments that expose them to new vectors of disease.

Population

No global estimates of abundance exist for Short-finned Pilot Whales; however, several regional population estimates indicate that in certain regions these species are relatively abundant, numbering from the thousands to hundreds of thousands. For example, Wade and Gerrodette (1993) estimated 160,200 Short-finned Pilot Whales in the eastern tropical Pacific, while more recently, Gerrodette and Forcada (2002) estimated 589,000 individuals in the same region. Indeed, Short-finned Pilot Whales have increased significantly in the eastern tropical Pacific from 1986–1990 to 1998–2000 (Gerrodette & Forcada 2002). In summer, south of the Antarctic Convergence, Waring et al. (2006) estimated approximately 200,000 Long-finned Pilot Whales, however this is expected to include some misidentified Short-finned Pilot Whales. No population estimates for Short-finned Pilot Whales are available for the assessment region. Model-based estimates of generation time are 23.5 years for Short-finned Pilot Whales (Taylor et al. 2007).

Current population trend: Increasing 

Continuing decline in mature individuals: Unknown  

Number of mature individuals in population: Unknown  

Number of mature individuals in largest subpopulation: Unknown   

Number of subpopulations: Unknown  

Severely fragmented: No 

Quantitative Analysis 

Probability of extinction in the wild within 3 generations or 10 years, whichever is longer, maximum 100 years: (Not specified) 

Probability of extinction in the wild within 5 generations or 20 years, whichever is longer, maximum 100 years: (Not specified) 

Probability of extinction in the wild within 100 years: (Not specified) 

Population Genetics

G. melas and G. macrorhyncus are genetically distinct at the species level, yet within species there are low levels of genetic (mtDNA) diversity reported (Oremus et al. 2009). Despite this evidence two distinct morphological forms have been identified within G. macrorhyncus based on stranded and hunted animals in Japan (Kasuyu et al. 1988; Oremus et al. 2009) – the “Shiho” form in the eastern Pacific Ocean and the “Naisa” form in the central/western Pacific and Indian Oceans as well as the Atlantic Ocean. However, a recent genetic study based on mitogenomes and SNP loci suggests there are three distinct subpopulations, with the Naisa form (or subspecies) actually separated into two diverging subpopulations: one in the Atlantic Ocean and the other in the western/central Pacific and Indian Oceans, separated by the Benguela Barrier off South Africa (Van Cise et al. 2019). As such, two genetically distinct subpopulations are known from the assessment region. Based on this information, the Convention on Biological Diversity’s Global Biodiversity Framework’s (GBF’s) complementary genetic indicator – proportion of populations maintained (PM) – would receive a value of 1.0 (all populations remaining). This is assuming no distinct subpopulations have gone extinct in the region.

While no global or regional population size estimates exist for Short-finned Pilot Whales, estimates from other regions suggest the species is relatively abundant, numbering from the thousands to hundreds of thousands (see Population section). The species would be considered genetically stable if approximately 5,000 individuals or more make up each of the two subpopulations, assuming a conversion ratio of Ne/Nc between 0.1-0.3 (i.e., ne > 500). In general, this is deemed to be feasible, especially considering both subpopulations are likely part of larger subpopulations within their respective waters with no additional barriers to gene flow likely to exist

Habitats and ecology

Short-finned Pilot Whales occur worldwide in tropical, subtropical and warm temperate waters and are present at highest densities over the continental shelf break, continental slope, and areas of high topographic relief. They are also found in deep, oceanographic environments. Although predominantly nomadic, resident populations are documented from the Canary Islands, Madeira Islands, coastal California, and the Hawaiian Islands. This species shows seasonal inshore/offshore movements reflecting that of its prey (squid and mackerel) and they have been recorded diving to depths over 1000 m (Reeves et al. 2003; Mintzer et al. 2008; Santos et al. 2014).

Cephalopods constitute a large proportion of the diet of Globicephala spp., and although fish are also consumed, they are predominantly adapted to a diet of squid. The stomach contents of four Short-finned Pilot Whales stranded at Port Elizabeth, South Africa were comprised of cephalopod remains including Loligo reynaudi and Oregoniateuthis (Ross 1984). Short-finned Pilot Whales perform deep dives, in the same depth range as Sperm and Beaked Whales, during the day and night off the Canary Islands, during which they produce click and buzz sounds associated with foraging (Aguilar de Soto et al. 2008). They also produce tonal and pulsed calls for social communication, with significant differences found between the two species. Short-finned Pilot Whales produce calls of a higher frequency and wider frequency range (mean 7879 Hz) than Long-finned (4480 Hz) and also have distinct group-specific repertoires (Olson 2018). 

Pilot Whales are considered extremely gregarious, occurring in average group sizes of 20-90 individuals although some groups can comprise several hundred (Oremus et al. 2009). Short-finned Pilot Whales in southern Africa varied in group size from two to 200 (mean 31.7) (Best 2007). They form strong and stable cohesive bonds with close matrilineal associations that may be an influencing factor in the occurrence of mass stranding events (Perrin & Geraci 2002; Alves et al. 2013). Pilot Whales are frequently observed in mixed-species groups, most commonly in association with bottlenose dolphins (Tursiops spp.). Short-finned Pilot Whales are fairly slow swimmers, and large groups have been recorded stationary on the surface of the water (Mitchell 1975). 

Although little is known about the reproductive biology of this species locally, in the northern hemisphere, breeding is seasonal, with births occurring in late summer (July/August) following a gestation period of 14.9 months (Skinner & Chimimba 2005). Female and male mature at an average length of 3.16 m (9 years old) and 4.14 m (16 years), respectively (Skinner & Chimimba 2005). Lactation periods vary greatly in Short-finned Pilot Whales (2 – 1 5 years) but are on average 3.5 -5.5 years (Best 2007). G. macrorhyncus shows a pronounced menopause (about 14 years), presumably driven by the sophisticated culture shown by the species, similarly to Killer Whales, Orcinus orca (Whitehead 2018). This allows for nonreproductive females to provide alloparental care (Kasuya, 1995). They are polygynous and it is thought that males move between female-led groups to mate during temporary aggregations comprising different family groups (Olson 2018)

Ecosystem and cultural services: Marine mammals integrate and reflect ecological variation across large spatial and long temporal scales, and therefore they are prime sentinels of marine ecosystem change (Moore 2008). 

IUCN Habitats Classification Scheme 

Habitat  Season  Suitability  Major Importance? 
10.1. Marine Oceanic -> Marine Oceanic – Epipelagic (0-200m)    Marginal   
10.2. Marine Oceanic -> Marine Oceanic – Mesopelagic (200-1000m)    Suitable  Yes 
10.3. Marine Oceanic -> Marine Oceanic – Bathypelagic (1000-4000m)    Suitable  Yes 

Life History 

(updated from Olsen 2018 & Best 2007) 

Generation Length: 23.5 years 

Age at Maturity: Female or unspecified: 9 years 

Age at Maturity: Male: 17-18 years 

Size at Maturity (in cms): Female: 316 cm; southern form 

Size at Maturity (in cms): Male: 422 cm 

Longevity: Females: 60 years; Males 35-45 years 

Average Reproductive Age: (Not specified) 

Maximum Size (in cms): Males: 520 cm; Females: 405 cm (Best 2007) 

Size at Birth (in cms): 140-185 cm, 55 kg 

Gestation Time: 14-16 months 

Reproductive Periodicity: 5-7 years 

Average Annual Fecundity or Litter Size: (Not specified) 

Natural Mortality: (Not specified) 

Does the species lay eggs? No 

Does the species give birth to live young: Yes 

Does the species exhibit parthenogenesis: No 

Does the species have a free-living larval stage? No 

Does the species require water for breeding? Yes 

Movement Patterns 

Movement Patterns: (Not specified) 

Congregatory: (Not specified) 

Systems 

System: Marine 

General Use and Trade Information

Although pilot whales in the northern hemisphere have been historically exploited for their oil, and are still hunted in regions such as Japan, there is no trade or use of this species within the assessment region. 

Subsistence:  Rationale:  Local Commercial:  Further detail including information on economic value if available: 
No       

National Commercial Value: No 

International Commercial Value: No 

End Use  Subsistence  National  International  Other (please specify) 
1. Food – human    true     
12. Handicrafts, jewellery, etc.    true     

Is there harvest from captive/cultivated sources of this species? (Not specified) 

Harvest Trend Comments: (Not specified) 

Threats

Due to their deep-water distribution, pilot whales within South African waters are not expected to experience any major threats that may severely impact their population status in the assessment region. However, additional research into the population status, taxonomy and seasonal movements of these species is needed, following which a reassessment of their conservation status may be necessary. A number of minor threats have been recognised: 

Bycatch, particularly in long-line squid fisheries, is a threat to Short- and Long-finned Pilot Whales. There is also a potential emerging threat posed by a southern shift in the distribution of effort by the tuna purse-seine fisheries. It is also possible that there is direct competition between the Long-finned Pilot Whale and the squid fishery, which has been documented in other parts of its range (Minton et al. 2018b), with both species widely reported to depredate on longline fisheries, removing fish from hooks during operations and losses to fisheries can be substantial (Werner et al. 2015).  Pilot whales are particularly susceptible to entanglement in driftnets, but the population-level effect of this mortality is unknown. Although, there is no local information available, commercial squid fisheries are widespread in the western North Atlantic, and the target species for these fisheries are squids commonly eaten by pilot whales, raising the possibility of prey depletion. Bernard and Reilly (1999) suggest that bycatch of pilot whales is likely to be considerably more common than is currently reported.

Similar to beaked whales, both species of pilot whales are thought to be vulnerable to anthropogenic noise pollution, specifically those produced by seismic exploration and navy sonar (Cox et al. 2006; Weir 2008; Antunes et al. 2014) but also increasing levels of commercial shipping and marine construction. Although, the cause of pilot whale mass stranding events remains controversial in many regions, Short-finned Pilot Whales are thought to be frequently impacted by high levels of anthropogenic marine noise (Hohn et al. 2006). As the intensity of marine noise pollution is thought to be increasing within South African waters (Koper & Plön 2012), this potentially represents an emerging threat. Similar to other deep-diving species, marine plastic pollution may also represent an emerging threat, as it has been shown to cause fatalities in sperm whales.

In addition to noise pollution, pilot whales are affected by chemical pollutants; in the north Atlantic long-finned pilot whales were found to have high levels of organochlorine and organobromide contaminants, which may impair reproduction and reduce disease resilience. Being predators at the top of the food chain, pilot whales also accumulate heavy metals such as cadmium and mercury in their meat and blubber and in Japan and the Caribbean the levels were considered unsafe for human consumption (Gajdosechova et al. 2016; Simmonds et al. 2002, Fielding and Evans 2014). 

Although the impacts of climate change to pilot whales are largely unknown, it is likely that changes in water temperature and CO2 concentration will have cascading effects on pilot whale movements and feeding ecology. Learmonth et al. (2006) reported that in the Faroe Islands, where Long-finned Pilot Whales have been historically hunted, catch rates were positively correlated with occurrence of a popular prey species, Todarodes sagittatus. This pelagic squid is thought to be either directly influenced by water temperature and CO2 concentration, or possibly indirectly influenced by productivity (Bjørge 2002). Additionally, environmental variation as a result of the 1982–1983 El Niño is likely to have indirectly caused the absence of Short-finned Pilot Whales, and their associated prey-species Loligo opalescens, in some regions.

Disease – The morbillivirus was responsible for the deaths of at least 60 G. melas in the Mediterranean (Bellière et al. 2011) and the impacts of climate change and ship-avoidance behaviour, may force the species into environments that expose them to other vectors of disease. Short-finned Pilot Whales are likely to be similarly affected. 

Although pilot whales are hunted in some parts of their range (for example, Long-finned Pilot Whales are caught in “drive-kill fisheries” off Japan and the Faroe Islands, Minton et al. 2018b; Olson 2018), these species are not hunted within the assessment region, and the small-scale exploitation in the southern hemisphere is considered to be irregular (Skinner & Chimimba 2005). 

Conservation

Both pilot whale species are listed in Appendix II of CITES and are protected in South Africa under the Threatened or Protected Species (TOPS) regulations that fall within the Marine Living Resources Act (Act 18 of 1998). No specific conservation measures can be recommended for these species within the assessment region until more information on population sizes, trends and threats are generated. As such, they would benefit from continued research into their population dynamics, distribution patterns and the impact of competition and bycatch with local squid fisheries. Globally, too, more research is needed to determine the impact of potential threats on pilot whales (Minton et al. 2018b).

Recommendations for managers and practitioners: 

  • Interactions between pilot whales and long-line fisheries require urgent investigation. The spatial distribution of squid fisheries and pilot whales should be mapped and overlaps identified. The impacts and severity of potential competition between the fisheries and the cetaceans should be quantified. 

Research priorities: 

  • The severity and potential impacts of threats, specifically the impacts of squid fisheries, could affect the listings of pilot whales. 
  • It is recommended that population census surveys are undertaken in South African waters, and Marion Island could be used as a monitoring base for G. melas. 
  • Data pertaining to these species’ distribution patterns and taxonomy is required. 

Encouraged citizen actions: 

  • Use information dispensed by the South African Sustainable Seafood Initiative to make good choices when buying fish in shops and restaurants, e.g. wwfsa.mobi, FishMS 0794998795. 
  • Save electricity and fuel to mitigate CO2 emissions and hence, the rate of climate change. 
  • Buy local products that have not been shipped. 
  • Sightings data from pelagic commercial tourism operators may be particularly valuable. 
  • Report any strandings to the relevant local authorities. 

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