true

ISRA FACTSHEETS

SOUTH AMERICAN ATLANTIC REGION

ISRA FACTSHEETS

SOUTH AMERICAN ATLANTIC REGION

Noronha ISRA

29/81

Noronha ISRA

Noronha

Summary

Noronha is located in the Fernando de Noronha Archipelago of Brazil. The area is characterised by coral reefs, rocky formations, sandy substrates, rocky shores, and deep oceanic zones. It is influenced by westward flow of the central South Equatorial Current, turbid waters, fronts, eddies, and wakes. Within this area there are: threatened species (e.g., Lemon Shark Negaprion brevirostris); reproductive areas (e.g., Atlantic Nurse Shark Ginglymostoma cirratum); feeding areas (e.g., Oceanic Manta Ray Mobula birostris); undefined aggregations (Whitespotted Eagle Ray Aetobatus narinari); and distinctive attributes (Caribbean Reef Shark Carcharhinus perezi).

Noronha

DESCRIPTION OF HABITAT

Noronha is situated in the Fernando de Noronha Archipelago, a set of 21 islands in the northeastern part of Brazil. The area encompasses Fernando de Noronha, the only human-inhabited and largest island in the area, which is 11 km in length and 3 km wide. It also includes some adjacent islands just off the coast of Fernando de Noronha including Rata Island. It is characterised by rocky outcrops, sandy and rocky substrates, coral reefs, seagrass beds, and underwater ridges (Matheus et al. 2019). The area is influenced by numerous water masses including the westward flow of the central South Equatorial Current, counter current, and undercurrent, which bring oxygen-rich and high-nutrient waters to the area from other locations (Matheus et al. 2019), including the Amazon River. The area is also influenced by turbid waters and fronts, eddies, and wakes which provide nutrient enrichment from deep to shallow waters, influencing local productivity (Matheus et al. 2019).

This Important Shark and Ray Area is benthic and pelagic and is delineated from inshore and surface waters (0 m) to 50 m based on the bathymetry of the area.

CRITERION A

VULNERABILITY

Six Qualifying Species considered threatened with extinction according to the IUCN Red List of Threatened Species regularly occur in the area. Threatened sharks comprise one Endangered species and two Vulnerable species; threatened rays comprise two Endangered species and one Vulnerable species (IUCN 2025).

CRITERION C

SUB-CRITERION C1 – REPRODUCTIVE AREAS

Noronha is an important reproductive area for two shark species and two ray species.

Neonate Atlantic Nurse Sharks have been regularly reported by recreational divers close to shore (up to 15 m depth). Animals were considered neonates based on the visual presence of small, dark, light-ringed ocellated spots. Neonates and young-of-the-year (YOY) have small black spots covering the entire body with alternating bands of lighter and darker pigmentation that occur before reaching 55 cm TL (Castro 2000). The reported size-at-birth of this species is 27–30 cm total length (TL) (Ebert et al. 2021). Neonates were reported in 1997 (n = 2), 2003 (n = 2), 2005 (n = 1), 2007 (n = 3), 2021 (n = 4), and 2024 (n = 1) (Garla et al. 2009, 2017b; VB Bettcher pers. obs. 2021–2024). They were observed hidden inside caves, crevices, seaweed banks, or colonies of octocorals. The use of these habitats makes opportunistic records difficult to obtain (Garla et al. 2017b). Additionally, between April–August 2015, 12 Atlantic Nurse Shark mating events were recorded in Sueste Bay within this area (Afonso et al. 2016). In July 2024, another mating event was opportunistically recorded within the area by recreational divers (VB Bettcher pers. obs. 2024). Finally, pregnant females aggregate in groups of 15–20 individuals (maximum ~45) regularly and predictably during the austral winter in this area (Garla et al. 2009; Afonso et al. 2016; VB Bettcher pers. obs. 2018–2024).

Aggregations of 3–12 neonate/YOY Lemon Sharks measuring 60–80 cm TL were observed every year between 2001–2007 at depths of up to 5 m along the intertidal zones (in areas of turbid waters over reef or rocky bottoms covered by brown algae) (Garla et al. 2009). In February 2023, three animals observed had open umbilical scars, measuring 62–68 cm TL (Garla et al. 2022). Between 2004–2019, females with mating scars as well as neonates/YOY were reported by citizen scientists (Garla et al. 2022). From 181 dives in the area, female Lemon Sharks with fresh mating scars were recorded during 22 dives (18%), pregnant females were recorded during 24 dives (19%), and one adult male with a fresh mating scar was observed (Garla et al. 2022). Neonate and YOY animals are observed underwater by recreational divers, site rangers, and from land-based viewpoints. The occurrence of neonate Lemon Sharks in this area is seasonal and occurs mostly between November–April within Sueste Bay, Leão Beach, and Santo Antônio Harbour, while YOY animals can be observed during the rest of the year (VB Bettcher pers. obs. 2021–2024). There are additional records of juvenile Lemon Sharks from the area. These young individuals have often been observed in aggregations and displaying feeding behaviour in shallow waters of at least one beach in the area (Garla et al. 2017a; B Rangel unpubl. data 2023). Lemon Shark aggregations of up to 15 individuals are observed feeding on sardine schools on the shore throughout the year, but mainly during the summer when their abundance is higher. Feeding aggregations of up to 12 juvenile Lemon Sharks have also been observed in the area at depths of 0.2–5 m along intertidal zones in turbid waters over reefs or rocky substrates covered by brown algae. The presence of neonates, YOY, and juvenile animals suggests that this area might be a nursery area for this species.

Reproductive activity of Lutz’s Stingray was opportunistically observed and recorded through scientific expeditions and citizen science contributions (Bettcher et al. 2022). Furthermore, mating behaviour was observed in 1997, 2008, 2014, 2018, 2021, 2022, and 2023 (Bettcher et al. 2022). All sightings of mating were made on the leeward side of Rata Island, within the area. Induced parturition was also recorded in a pregnant female incidentally caught in the area in May 2022 at a depth of 40 m (Bettcher et al. 2022). The cloaca was darker and dilated, and parturition began before the ray was released. The litter consisted of two well-developed pups, with an estimated 25 cm DW (Bettcher et al. 2022). Females with mating scars and distended abdomen indicating pregnancy are also regularly (every year) recorded by recreational divers (VB Bettcher pers. obs. 2021–2024).

Between 2014–2019, 79 Oceanic Manta Rays were reported in the area by citizen scientists undertaking recreational dives (Bucair et al. 2021; N Bucair unpubl. data 2025). Of these, 53 were measured by a trained observer. The majority of the measured animals (83%, n = 44) were considered neonate/YOY, and estimated to measure between 150–200 cm disc width (DW). The size-at-birth for this species is unknown, however, there are observations of individuals measuring ~140 cm DW (Bucair et al. 2021) and <100 cm DW (Gomes de Souza 2022) outside of this area. The size-at-birth is 130–150 cm DW for the smaller congeneric Reef Manta Ray Mobula alfredi (Last et al. 2016). No mature individuals were reported and the other nine animals observed were considered juveniles or sub-adults measuring 220–300 cm DW (Bucair et al. 2021; N Bucair unpubl. data 2025). Oceanic Manta Ray males mature at ~375–400 and females at 410–470 cm DW (Last et al. 2016). Most reports were made between April–October, however, further information is required to determine the seasonality of the reproductive importance of this area. Individuals were sighted repeatedly across numerous seasons and years (Bucair et al. 2021). These records likely represent animals of a putative species (Mobula cf. birostris).

CRITERION C

SUB-CRITERION C2 – FEEDING AREAS

Noronha is an important feeding area for one shark species and one ray species.

Lemon Sharks use specific sites in this area to aggregate throughout the year to feed on sardines Harengula clupeola (Garla et al. 2017a; B Galvão pers. obs. 2024; VB Betcher pers. obs. 2025; R Ostrovski pers. obs. 2025; B Rangel pers. obs. 2025). Feeding behaviour is recorded at around 5 m depth around Bode Beach, Sueste Beach, and Conceição Beach. This behaviour was recorded each year when cliff-top visual surveys were undertaken: 2006 (n = 1 feeding observation), 2012 (n = 1), and 2013 (n = 5). Between April 2008–December 2009, hunting behaviour was recorded in 136 events at Conceição Beach in the area (65.4% of all observations) during snorkelling surveys. At Sueste Beach, hunting behaviour was recorded in 10 instances. There appears to be no seasonality in the observation of hunting behaviour at these sites (Garla et al. 2017a). Whilst the aforementioned records report Lemon Sharks feeding in aggregations of up to three individuals, more recent records report feeding behaviour of Lemon Sharks in aggregations of up to 25 animals. Feeding observations have been recorded from cliff-top surveys and snorkellers each year between 2022–2025 (B Rangel pers. obs. 2022–2025; B Galvão pers. obs. 2024; VB Betcher pers. obs. 2024–2025; R Ostrovski pers. obs. 2025).

This area is one of the only known locations in Brazil where Oceanic Manta Rays are regularly and predictably observed feeding. From 79 sightings reported by citizen scientists during recreational dives, behaviour was recorded for 62 animals (Bucair et al. 2021; N Bucair unpubl. data 2025). Of these, almost half of the animals (41.9%, n = 26) were displaying feeding behaviour. Only two individuals were feeding offshore, outside of this area, while the vast majority were inshore. These reports were made in 2016 (n = 9), 2017 (n = 10), and 2019 (n = 6).  The oceanic conditions that influence this area appear to be creating ideal feeding conditions for this species (Bucair et al. 2021; N Bucair unpubl. data 2025). These upwelling conditions appear to increase primary productivity and enrich the inshore waters which are protected from currents and winds. This area is used repeatedly for feeding purposes by the same individuals in different seasons for several years (Bucair et al. 2021).

CRITERION C

SUB-CRITERION C5 – UNDEFINED AGGREGATIONS

This is an important area for undefined aggregations of one ray species.

Recreational divers have regularly observed Whitespotted Eagle Rays aggregating at two sites in the area: Rata Channel and Santo Antônio Harbour. At Rata Channel, Whitespotted Eagle Rays were reported in groups of 3–9 individuals (N Bucair unpubl. data 2025). These aggregations were reported in 2006 (n = 2), 2008 (n = 1), 2009 (n = 1), and 2011 (n = 3), generally between March and August. Dives have been undertaken in Rata Channel approximately once per day since 2002–2005 (N Bucair unpubl. data 2025). At Santo Antônio Harbour, Whitespotted Eagle Rays aggregate in groups of 3–27 individuals (N Bucair unpubl. data 2025). These aggregations have been recorded in 2016 (n = 4), 2017 (n = 6), and 2018 (n = 2), also mostly during winter (April–September). Recreational dives have been undertaken in Santo Antônio Harbour every day since 2015. Further information is required to determine the nature and function of these aggregations.

CRITERION D

SUB-CRITERION D1 – DISTINCTIVENESS

Noronha is a distinctive area for one shark species.

This area is an important resting area for Caribbean Reef Sharks and is the only known area within the region where this species is regularly and predictably observed resting motionless; usually in caves away from strong water currents (N Bucair unpubl. data 2025). Recreational divers have also reported observations of Caribbean Reef Sharks resting laterally on social media. Outside of this region, this species has only been observed resting on its stomach in Mexico (Aldora Divers 2025) and the Bahamas (Doug Perrine Photography 2025; Florida Museum 2025). Recreational divers have reported nine instances of this distinct behaviour, in 2008 (n = 1), 2009 (n = 4), 2011 (n = 1), 2016 (n = 1), 2018 (n = 1), and 2019 (n = 1). All observations were of animals resting alone. Observations have been reported from numerous locations within the area (e.g., Laje Dois Irmãos, Pontal do Norte, and Caverna da Sapata; N Bucair unpubl. data 2025).

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