Research Article |
Corresponding author: Alexandra Fernandes Costa ( alexandrafernandescosta@gmail.com ) Academic editor: Pavel Stoev
© 2017 Alexandra Fernandes Costa, Salvatore Siciliano, Renata Emin-Lima, Bruna Maria Lima Martins, Maura Elisabeth Moraes Sousa, Tommaso Giarrizzo, José de Sousa e Silva Júnior.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Costa AF, Siciliano S, Emin-Lima R, Martins BML, Sousa MEM, Giarrizzo T, Silva Júnior JS (2017) Stranding survey as a framework to investigate rare cetacean records of the north and north-eastern Brazilian coasts. ZooKeys 688: 111-134. https://doi.org/10.3897/zookeys.688.12636
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Marine mammal stranding events are used as an important tool for understanding cetacean biology worldwide. Nonetheless, there are vast gaps of knowledge to be filled in for a wide range of species. Reputable information is required regarding species from large baleen whales to sperm and beaked whales, as well as pelagic dolphins. This paper describes new cetacean records from north and north-eastern Brazil, which are both the least surveyed areas regarding aquatic mammals. Regular beach surveys were conducted to recover cetacean carcasses along the coast of Pará beginning November 2005. At the coasts of the Maranhão and Piauí states, the surveys were conducted between 2003 and 2013. From 2003 to 2014, 34 strandings of cetaceans were registered. The study provides four additional species records’ in the area based on strandings (Balaenoptera borealis, Balaenoptera physalus, Peponocephala electra, and Pseudorca crassidens). A mass stranding of Guiana dolphins (Sotalia guianensis, N = 12), the most common species for the region, was reported for the first time. The records presented herein are of special concern, since they expand the knowledge on cetaceans from the Brazilian coast. In addition, this study conducted an analysis to verify the similarity between cetacean compositions described for north and north-eastern Brazil and the southern Caribbean region. The results showed a high similarity between these regions, proving the connection with the Caribbean cetacean fauna.
Amazon, Balaenopteridae , beach survey, cluster analysis, Delphinidae , marine mammals distribution, Physeteridae , South America
The Amazon Coastal Zone (ACZ), between 4°N and 4°S, presents a singular environment, characterized by the immense discharge of the Amazon River. ACZ is an unique aquatic ecosystem where the largest continuum of mangrove belt of the world is found (
The cetacean fauna of Brazil has been subject to an extensive number of groups dedicated to conservation and research issues since the 1980’s. Because of this, a considerable amount of new information on cetacean distribution, biology and ecology has arisen (e.g.
Nevertheless, there are vast gaps of knowledge to be filled in for a wide range of species. From large baleen whales to sperm and beaked whales, as well as pelagic dolphins, reputable information is required. This is due, in part, to the lack of inventories over large areas of the Brazilian coast.
Studies on the occurrence of cetaceans around the world are made using different methodologies such as: strandings, historical records, opportunistic sightings, and dedicated surveys (
The main goals of this report are to: (1) present a variety of new cetacean records along the northern Brazilian coast, (2) increase baseline information on cetacean occurrence over 11 years (2003–2014); and (3) compare the cetacean composition in distinct areas along the north and north-eastern Brazilian coasts with southern Caribbean region, investigating the similarity between these sectors. The results of this study could open a promising new window for understanding the cetacean community structure in this vast stretch of coast.
The northern Brazilian coast has Cabo Orange as its limits to the north (05°N, 51°W), and São José Bay to the south (02°S, 44°15'W) and represent the Atlantic coastal sector. This vast coastal area extends for approximately 2250 km composed of different systems: mangrove forests, salt marshes, tidal sand flats, chenier sand ridges, coastal dunes, beach ridge barriers, and ebb tidal delta (
The study site of this report is divided into three sampling sectors: (1) Marajó Bay (MB), (2) Eastern Pará state (EP) and (3) Maranhão/Piauí coastline (MA/PI), encompassing part of Parnaíba Delta (Fig.
Marajó Bay is located on the eastern coast of Marajó Island (Fig.
In the eastern coast of Pará (Fig.
Study sites. Surveyed sectors on north and north-eastern Brazilian coast: 1 Marajó Bay 2 Eastern Pará state and 3 Maranhão and Piauí coastlines encompass part of Parnaíba Delta. Black dots representing stranding locations. Physeter macrocephalus (Pma), Balaenoptera brydei (Bbr), Balaenoptera physalus (Bph), Megaptera novaeangliae (Mno), Steno bredanensis (Sbr), Balaenoptera borealis (Bbo), Tursiops truncatus (Ttr), Globicephala macrorhynchus (Gma), Pseudorca crassidens (Pcr), Sotalia guianensis (Sgu), Peponocephala electra (Pel), Stenella attenuata (Sat), Lagenodelphis hosei (Lho), Delphinus sp. (Dsp) and Grampus griseus (Ggr).
Maranhão and Piauí coastlines, encompassing the Parnaíba Delta (Fig.
Stranding events in these areas were regularly monitored between 2005 and 2014 in MB and EP sampling sectors, and from 2003 to 2013 in MA/PI sector (Fig.
On occasion, the team was called to respond to live strandings or carcasses washed ashore. These events, as they are exclusive in their nature and circumstances, are validated with voucher samples, photographs, and other sources of original information.
The carcasses were identified in the field following specific features (e.g. colouration, shape of the head and fins/flippers, number of teeth). In such specific cases as Delphinus sp. and Megaptera novaeangliae, the identification was made posteriorly through cranial measures and scapular features, respectively.
Complete and incomplete carcasses were recovered and their skeletons and soft tissues, after preparation, are deposited at the Mammal Collection from Museu Paraense Emílio Goeldi (
Species by Family | Category | TL (m) | Sex | Sector | Date | Voucher specimens |
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Balaenopteridae | ||||||
Balaenoptera borealis | LS | 10.32 | F | EP | 13/09/2008 |
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Balaenoptera brydei | CA | 4.20 | NI | MB | 15/09/2012 |
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Balaenoptera physalus | LS | 14.90 | M | EP | 21/01/2010 |
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Megaptera novaeangliae | CA | 16.70 | F | MA/PI | 15/01/2003 | - |
CA | - | NI | MA/PI | 2005 | - | |
CA | 10.00* | M | EP | 08/10/2008 |
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CA | 13.00* | NI | MA/PI | 22/05/2009 |
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Physeteridae | ||||||
Physeter macrocephalus | CA | 11.80 | F | MA/PI | 02/02/2010 |
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CA | - | F | MA/PI | 14/05/2010 |
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LS | 10.50 | F | EP | 07/04/2014 |
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CA | 4.22 | NI | MB | 08/08/2014 |
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Delphinidae | ||||||
Delphinus sp. | CA | 2.06 | NI | MA/PI | 12/08/2011 |
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Globicephala macrorhynchus | CA | - | NI | MA/PI | 2009 | - |
CA | - | NI | MA/PI | 15/01/2009 |
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Grampus griseus | CA | - | NI | MA/PI | 13/04/2011 |
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Lagenodelphis hosei | LS | - | M | MA/PI | 03/04/2009 |
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Peponocephala electra | CA | - | NI | MA/PI | 2007 |
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CA | - | NI | MA/PI | 19/06/2008 |
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Pseudorca crassidens | CA | 3.30 | NI | EP | 20/04/2012 |
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Sotalia guianensis | LS | - | NI | EP | 31/01/2013 | - |
Stenella attenuata | CA | - | NI | MA/PI | 14/03/2009 |
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CA | 1.59 | M | MA/PI | 10/12/2009 |
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Steno bredanensis | CA | - | NI | EP | 19/04/2009 |
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CA | - | NI | MA/PI | 15/08/2011 |
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CA | - | NI | EP | 20/11/2011 |
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CA | - | NI | EP | 20/11/2011 |
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CA | 2.68 | M | EP | 04/04/2012 |
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CA | - | NI | MA/PI | 23/08/2013 |
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Tursiops truncatus | CA | - | NI | MA/PI | 24/04/2009 |
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CA | - | NI | MA/PI | 26/07/2009 |
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CA | - | NI | MA/PI | 05/03/2010 | - | |
CA | - | NI | EP | 12/03/2010 |
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CA | 3.17 | M | EP | 13/02/2013 |
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CA | 2.87 | F | EP | 04/03/2013 |
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The similarity between the cetacean composition described in this study and the most representative surveys conducted in the north (
Similarities between the stranding and sighting records of cetaceans reported in seven articles and the present study was accomplished through an analysis of similarity by the Jaccard index based on the presence or absence of species. A similarity profile (SIMPROF) test was performed to detect the significantly different groups using the default of 1.000 permutations for the mean similarity profile and 999 permutations for the simulated profile, with a significance level of 0.05. Multivariate analyses were performed using PRIMER 6.0 (PRIMER-E Ltd., Plymouth, U.K) (
The present study recorded rare strandings of some cetacean species (e.g. mass stranding of Sotalia guianensis), and the first occurrence of these cetaceans in northern coast: 1. Sei whale, Balaenoptera borealis Lesson, 1828, 2. Fin whale, Balaenoptera physalus (Linnaeus, 1958), 3. Melon-headed whale, Peponocephala electra (Gray, 1846) and 4. False killer whale, Pseudorca crassidens (Owen, 1846).
Species richness was represented for 15 taxa, within three distinct families: Balaenopteridae (B. borealis, B. physalus, B. brydei, M. novaeangliae), Physeteridae (P. macrocephalus) and Delphinidae (Delphinus sp., G. macrorhynchus, G. griseus, Lagenodelphis hosei, P. electra, P. crassidens, S. guianensis, S. attenuata, S. bredanensis, T. truncatus) (Table
In these sampling sectors (MB = Marajó bay; EP = Eastern Pará; MA/PI = Maranhão/Piauí coastline) stranding events were distributed unequally. The spatial distribution among sectors showed that the majority of strandings occurred at the Maranhão/Piauí coastline 54.5% (N = 18), on the north-eastern coast of Brazil. The EP occupies the second place, with 39.4% (N = 13) and MB with only 6.1% (N = 2) of rare cetacean records.
Differences in strandings by family and sector were analyzed in order to evaluate patterns along the distinct sectors of this coastline. Members of the Delphinidae family were the most representative in the frequency of strandings, comprising 66.7% (N = 22), followed by Balaenopteridae 21.2% (N = 7) and Physeteridae 12.1% (N = 4).
Sei whale
On 13 September 2008 a large whale stranded alive on the eastern Pará state (EP). The specimen (
Stranding events: large baleen whales. a Fin whale Balaenoptera physalus stranded at Baía do Japerica, São João de Pirabas municipality (0°45'S, 47°4.2'W), eastern coast of the Pará state. Note the good condition of the carcass and the strange swelling on the top of the head (see white arrow) (photo by GEMAM/
Bryde’s whale
On 15 September 2012 a decomposed carcass of a newborn B. brydei washed ashore on the rocky shore of Praia de Água Boa, Salvaterra, Marajó bay (MB), Pará (Fig.
Fin whale
On January 2010, a male Fin whale B. physalus was reported stranded on the eastern Pará state (EP) in Baía do Japerica, São João de Pirabas municipality. Fishermen and residents sighted the live specimen entering the estuary but a few days later the carcass was found stranded in a different location. The fresh specimen had a large callosity on the top of the head (Fig.
Humpback whale
The first evidence of a Humpback whale M. novaeangliae in Piauí is represented by a female stranded at Praia da Pedra do Sal, Parnaíba on 15 January 2003. Subsequently, in 2005, locals collected a scapula at Praia da Carnaubinha, Luís Correia municipality. On May 2009, a decomposed carcass missing the skull was found stranded in the Praia do Rio Novo, Tutóia municipality, voucher No
Sperm whale
On 02 February 2010 a female with TL = 11.80 m (
Stranding events: sperm whales. a Sperm whale Physeter macrocephalus (
Common dolphin
On 12 August 2011 a decomposed delphinid carcass was found at Praia da Pedra do Sal, Parnaíba municipality, Piauí (MA/PI coastline) (
Fraser’s dolphin
On the coast of the Maranhão state, at Praia da Barrinha, Canárias Island, the carcass of a Fraser’s dolphin Lagenodelphis hosei was found fresh by fishermen on 03 April 2009, after it presumably live-stranded on the beach. The carcass was divided up at the village of Carnaubeira, Araioses municipality (Fig.
Stranding events: small and medium-sized cetaceans. a The carcass of a Fraser’s dolphin, Lagenodelphis hosei was cut down on the village of Carnaubeira, Araioses municipality (2°42.6'S, 42°0.6'W) and consumed locally (photo PROCEMA files) b A group of 12 live Guiana dolphins Sotalia guianensis were found trapped (photo showed just one specimen) in a tidal channel alongside Corvina beach, Salinópolis municipality, eastern Pará (0°36'S, 47°22.2'W) c A False killer whale Pseudorca crassidens stranded on the north-eastern coast of Pará, Praia de Marudá, Marapanim municipality (photo GEMAM files) d A Short-finned pilot whale Globicephala macrorhynchus stranded in advanced stage of decomposition at Praia da Pedra do Sal, Parnaíba municipality (2°40.8'S, 42°31.2'W), the shape of the head and number of teeth were diagnostic to identify the species (photo PROCEMA files).
Pantropical spotted dolphin
The Pantropical spotted dolphin S. attenuata is represented by two records from the MA/PI sector, both from 2009. Bone remains were found at the Canárias Island, Praia da Barrinha, Maranhão (
A Short-finned pilot whale Globicephala macrorhynchus Gray, 1846 was found stranded in an advanced state of decomposition in the Parnaíba municipality, Piauí (MA/PI), on 15 January 2009 (
An incomplete Risso’s dolphin skull Grampus griseus (G. Cuvier, 1812) (
Two stranding records of Melon-headed whale Peponocephala electra (Gray, 1846) were reported for the Ilha do Caju and Delta do Parnaíba (MA/PI). Only bone remains were recovered (
The first record of a False killer whale Pseudorca crassidens (Owen, 1846) on the Pará coastline occurred on 20 April 2012. The carcass was found in the mudflats at Praia de Marudá (Fig.
Guiana dolphin
On 31 January 2013, 12 Guiana dolphins S. guianensis were reported as trapped in a tidal channel alongside Praia da Corvina, Salinópolis municipality, eastern Pará state (Fig.
Rough-toothed dolphin
On 04 April 2012, the carcass of a mature male (
Bottlenose dolphin
Five new records of Bottlenose dolphin T. truncatus were reported after the previous review by
The cluster analysis indicated that the cetacean composition from the Caribbean and north Brazilian coast form a single group (Group 1) that differs significantly from the group formed at north-eastern Brazil (Group 2) (Fig.
Cluster analysis of cetacean stranding and sighting records. Diagram of cetaceans reported from the north-eastern (inverted triangle) and north coast of Brazil (triangle) and southern Caribbean (square), reported in seven articles and the present study. The two distinct groups formed (Group 1 and 2) are indicated. A similarity profile (SIMPROF) permutation test highlights dashed clusters that show significant internal structure. Shaded cells indicate occurrence of species.
The richness of species varied from 13 to 24, with 29 species in totality. Group 2 was defined by adding stranding information from north-eastern Brazil (
Stranding data are an important source to understanding the biology and ecology of marine mammals (
Localities of marine mammal strandings and other localities mentioned in this study.
Locality | Municipality | Lat / Long | Description (species, others) |
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Cabo Orange | Oiapoque | 5°N, 51°W | northern Brazilian coast to the west |
Ponta do Tubarão | Baía de São José | 4°00'S, 43°00'W | northern Brazilian coast to the east |
Fernandes Belo | Viseu | 1°10.8'S, 46°5.4'W | Balaenoptera borealis |
Praia de Água Boa | Salvaterra | 0°51.6'S, 48°30'W | Balaenoptera brydei |
Baía do Japerica | São João de Pirabas | 0°45'S, 47°4.2'W | Balaenoptera physalus |
Praia da Pedra do Sal | Parnaíba | 2°49.15'S, 41°42.8'W | Megaptera novaeangliae |
Praia da Carnaubinha | Luís Correia | 2°54.77'S, 41°30.66'W | Megaptera novaeangliae |
Praia do Rio Novo | Tutóia | 2°42.6'S, 42°26.4'W | Megaptera novaeangliae |
Praia de Fora | Quatipurú | 0°44.4'S, 46°57'W | Megaptera novaeangliae |
Praia da Pedra do Sal | Parnaíba | 2°49.8'S, 41°41.4'W | Physeter macrocephalus |
Praia do Baixo da Boia | Paulino Neves | 2°37.2'S, 42°38.4'W | Physeter macrocephalus |
Praia do Crispim | Marapanim | 0°34.8'S, 47°38.4'W | Physeter macrocephalus |
Praia do Camburupy | Soure | 0°32.4'S, 48°28.2'W | Physeter macrocephalus |
Praia da Pedra do Sal | Parnaíba | 2°47.4'S, 41°45'W | Delphinus sp. |
Praia da Barrinha | Araioses | 2°42.6'S, 42°0.6'W | Lagenodelphis hosei |
Praia da Barrinha | Araioses | 2°42.6'S, 42°0.6'W | Stenella attenuata |
Praia da Pedra do Sal | Parnaíba | 2°47.4'S, 41°45'W | Stenella attenuata |
Praia da Pedra do Sal | Parnaíba | 2°49.8'S, 41°41.4'W | Globicephala macrorhynchus |
Paulino Neves | Paulino Neves | 2°40.8'S, 42°31.2'W | Globicephala macrorhynchus |
Praia da Pedra do Sal | Parnaíba | 2°49.8'S, 41°42'W | Grampus griseus |
Delta do Parnaíba | - | - | Peponocephala electra |
Ilha do Caju | Araioses | 2°41.4'S, 42°5.4'W | Peponocephala electra |
Praia de Marudá | Marapanim | 0°37.2'S, 47°37.8'W | Pseudorca crassidens |
Praia da Corvina | Salinopólis | 0°36'S, 47°22.2'W | Sotalia guianensis |
Praia de Ajuruteua | Bragança | 0°49.2'S, 46°36'W | Steno bredanensis |
Praia da Princesa | Maracanã | 0°34.2'S, 47°34.8'W | Steno bredanensis |
Praia do Crispim | Marapanim | 0°34.8'S, 47°38.4'W | Steno bredanensis |
Praia do Crispim | Marapanim | 0°34.8'S, 47°38.4'W | Steno bredanensis |
Praia da Pedra do Sal | Parnaíba | 2°49.2'S, 41°42.6'W | Steno bredanensis |
Praia da Pedra do Sal | Parnaíba | 2°48'S, 41°43.8'W | Steno bredanensis |
Praia da Princesa | Maracanã | 0°34.2'S, 47°34.8'W | Tursiops truncatus |
Praia da Moita Verde | Araioses | 2°43.8'S, 41°48'W | Tursiops truncatus |
Furo Velho | Maracanã | 0°35.4'S, 47°33'W | Tursiops truncatus |
Porto do Sossego | Marapanim | 0°36.6'S, 47°37.8'W | Tursiops truncatus |
Praia da Travosa | Santo Amaro | 2°21'S, 43°15'W | Tursiops truncatus |
Baía do Capim | - | 1°76'S, 44°83'W | Sperm whale stranding at Maranhão coast |
The spatial distribution of species in the three sectors (MB, EP and MA/PI coastline) provides relevant information on their occurrence through stranding notifications. Small pelagic and neritic-pelagic cetaceans have been recorded in higher numbers along the EP and MA/PI sectors. In contrast, the MB area and adjacent coastline are influenced by the Amazon and Pará/Tocantins Rivers discharges, thus presumably limiting the occurrence and subsequent stranding of pelagic species. It should be considered that areas of difficult access and sparsely populated in the Amazon coastal zone, as the eastern Pará and the western Maranhão states, could represent potential circumstances for the low stranding notifications in these sectors. Although the systematic monitoring effort was lower at Maranhão/Piauí coastline, this area resulted to be singular due to the exclusive cetacean records of pelagic and neritic-pelagic species (e.g. Lagenodelphis hosei, Peponocephala electra). Despite the surveys were more dedicated in the MB sector, the frequency of uncommon strandings (e.g. oceanic species) were lower. However, single strandings of Sotalia guianensis, Inia geoffrensis and I. araguaiaensis in MB are not included in this report as they are commonplace and will be analyzed separately.
Earlier records of balaenopterids on the Amazon coastal zone were performed by
The newborn Bryde’s whale recorded in Praia da Água Boa (MB) on 15 September 2012 is a remarkable record, since very limited information exists on the pregnancy and time of birth of this tropical balaenopterid and, in Brazil, information on the calving season is almost non-existent (
In relation to odontocetes, four additional Sperm whales records are included from the Pará state and Maranhão/Piauí coastlines. One of them is of a very young specimen (TL = 4.22 m) stranded at east coast of the Marajó Island. This record strongly suggests the existence of calving off in the northern Brazilian coast. Sperm whales are a regular component of cetaceans found stranded on the north-eastern coast of Brazil. For example,
Blackfish records were represented by the False killer whale, Melon-headed whale, Short-finned pilot whale, and Risso’s dolphin recovered in distinct areas. These specimens improve the knowledge on blackfish occurrence off the northern Brazilian coast. The False killer listed in this study is noteworthy; this is the first record of this species in the region. The specimen (
The records of Bottlenose, Rough-toothed, and Common dolphins indicate their regular presence in neritic waters off northern Brazil, where then are referred by the fishermen as ‘tuninas’. The Common dolphin specimen recorded at Praia da Pedra do Sal is certainly of special interest as so little is known of this population inhabiting the north-eastern coast (see
The evidence of consumption of a fresh Fraser’s dolphin denotes further investigation on the use of marine bushmeat along small fishing communities of north-eastern Brazil.
Regarding coastal species, a mass stranding of Guiana dolphins was reported for the first time, based on an incident recorded in Salinópolis (EP), on January 2013. The coastline of Pará possesses certain unique features, such as very strong tides that cause accelerated movement of the sand banks and tidal channels. It seems plausible to believe in a natural condition characterized by this muddy beach and fast lowering tide acting as a trap. Although Guiana dolphins are familiar with flat waters and tide dynamism, the particular location of the Praia da Corvina could have acted as a natural trap. Nonetheless, the singularity of this event is worth mentioning and adds a new feature to the natural behavior of Guiana dolphins.
The cetacean fauna off the north and north-eastern Brazilian coast is much richer and diverse that previously thought, including both residents of tropical oligotrophic waters and highly-migrating baleen whales. Species associated to productive environments are also included, such as Bryde’s whales and the Common dolphin. As pointed out by the present survey, the connection with the southern Caribbean cetacean fauna seems plausible and deserves further investigation. This is particularly relevant for understanding the affinity of north Brazilian Bryde’s whale and Common dolphin populations with the adjacent Venezuela regional aggregations of these species (Galindo 2007). There is a lack of information on countries of Wider Caribbean Region as Guyana, Suriname, and French Guiana, however, surveys developed at Guiana’s coastal province supply important records on cetacean composition (Manocci et al 2013, Boer 2015). Such a relationship is highly expected and could potentially connect the north Brazilian cetacean fauna with that from the southern Caribbean.
Strandings of uncommon cetacean species and a live beached Sperm whale are recorded for the first time along the north coast of Brazil. Balaenopterids records (Balaenoptera borealis and B. physalus) presented herein are of particular importance and include the very first of its category on the northern coast of Brazil providing new insights on migration movements on the southern hemisphere.
Evidence of anthropogenic injuries inflicted to cetaceans and also the consumption of marine bushmeat is reported to the north-eastern coast of Brazil. Although the proximity of the northern and the north-eastern Brazilian coasts, results showed that cetacean fauna in northern is more similar with the Caribbean region. Further investigation on movements and distribution patterns should be encouraged.
In this context, beach surveys and stranding network definitely provide relevant information on marine mammals’ richness and diversity is this vast region. The cetacean fauna of north and north-eastern Brazil combines different elements from tropical marine ecosystems under the influence of the most powerful river of the world. Such dynamism requires a proportional research effort to better evaluate and understand its own complexity.
We would like to thank the GEMAM members who helped with field surveys, carcass collections, and processing at the Pará coast. AF Costa is indebted to Herbert Freitas (Quadrado) for his support and the collections made at the Piauí coast, without his help we would not have obtained the diversity of cetaceans in that sector. We are grateful to veterinarians Dr Valíria Cerqueira and Dr Pedro Bezerra and their staff from the Universidade Federal do Pará/Instituto de Medicina Veterinária-Campus Castanhal for their assistance in necropsies and staff of NUBIO/IBAMA/SUPES/PA for all the logistic and technical support for the stranding callings. Thanks to the staff of the
This study was supported by VALE/FAPESPA/FAPEMIG (Process no. 038/2011) and Petrobras (Projeto Bicho D’água: Conservação Socioambiental and Projeto Cetáceos do Maranhão). M Sousa received a scholarship from Coordenação de Aperfeiçoamento de Pessoal de Nível Superior-CAPES. T Giarrizzo is funded by CAPES (PNPD), and receives a productivity grant from Conselho Nacional de Desenvolvimento Científico e Tecnológico-CNPq (310299/2016-0). This article is part of Alexandra Costa’s PhD thesis in Aquatic Ecology and Fishery from the Universidade Federal do Pará. CAPES provided the scholarship for AF Costa during PhD course. Programa de Capacitação Institucional (
S1 Movie
Data type: MOV file
Explanation note: Dolphins trapped at Praia da Corvina, Salinópolis (MOV).
S2 Movie
Data type: MOV file
Explanation note: Rescue Guiana dolphins trapped at Praia da Corvina, Salinópolis (MOV).
S3 Movie
Data type: MOV file
Explanation note: Dolphin stranded at Praia da Travosa, Santo Amaro (MOV)