true

ISRA FACTSHEETS

SOUTH AMERICAN ATLANTIC REGION

ISRA FACTSHEETS

SOUTH AMERICAN ATLANTIC REGION

Golfo Nuevo ISRA

74/81

Golfo Nuevo ISRA

Golfo Nuevo

Summary

Golfo Nuevo is located in the northeast of Chubut Province in Argentina. The area encompasses the western and central areas of the gulf that is formed by the Carlos Ameghino Isthmus with the Peninsula de Valdés. It is characterised by sandy substrates and rocky reefs and is influenced by a strong austral summer stratification. Within the area there are: threatened species and undefined aggregations (Tope Galeorhinus galeus).

Golfo Nuevo

DESCRIPTION OF HABITAT

Golfo Nuevo is located in the northeast of Chubut Province in Argentina. The area is situated south of the Carlos Ameghino Isthmus, which connects the Peninsula de Valdés with the continent. The gulf is 56 km long and 40 km wide, with a 16 km wide entrance, and reaches depths of up to 170 m at its entrance. The area is characterised by sandy substrates and rocky reefs. It is influenced by a strong summer stratification, with cool benthic water temperatures of 11–12ºC and warmer surface waters of 16–17ºC (Rivas & Pipa 1989). The tidal regime in Golfo Nuevo is semidiurnal, with mean amplitudes of 4.7 m and 2.9 m (Villaverde et al. 1974).

This Important Shark and Ray Area is benthic and pelagic and is delineated from inshore and surface waters (0 m) to 110 m based on the bathymetry of the area.

CRITERION A

VULNERABILITY

One Qualifying Species considered threatened with extinction according to the IUCN Red List of Threatened Species regularly occurs in the area. This is the Critically Endangered Tope (Walker et al. 2020).

CRITERION C

SUB-CRITERION C5 – UNDEFINED AGGREGATIONS

Golfo Nuevo is an important area for undefined aggregations of one shark species.

Tope aggregates seasonally during the austral summer and early autumn in the area. In 2011, 2012, 2015, and 2017 scientific surveys captured and tagged Tope using a longline at a depth between 80–110 m. Between 2011–2012, a total of 17 fishing trips were conducted, with at least one fishing day per month. A bottom-set longline measuring between 500–1,200 m, with hooks spaced every 10 m, was deployed for a maximum duration of 120 min (Irigoyen et al. 2015). Captured Tope were sexed, tagged using traditional dart tags, and their sizes were visually estimated. Catch-per-unit-effort (CPUE) was used to calculate the relative abundance as individuals captured hooks-1 h-1. A total of 228 Tope were captured (129 females, 98 males, and one undefined) with higher values of CPUE (0.20 captures hooks-1 h-1) during summer and early autumn compared to the CPUE ranging from 0.13–0.02 during the rest of the year (Irigoyen et al. 2015).

Additionally, in 2015 (n = 3) and 2017 (n = 1), scientific fishing days were conducted during February and March using an 800 m bottom longline equipped with 110 baited hooks and set for 120 min (Jaureguizar et al. 2018; A Irigoyen unpubl. data 2025). Across these fishing days, a total of 13, 63, and 14 individuals were captured respectively in 2015, while 36 individuals were captured during one fishing day in 2017 (Jaureguizar et al. 2018; A Irigoyen unpubl. data 2025). The individuals measured 90–150 cm total length (TL) (A Irigoyen unpubl. data 2025). These sizes indicate that individuals captured were immature or subadults, as the species reaches maturity at ~120–170 cm TL for males and 130–185 cm TL for females (Ebert et al. 2021). During the same period, three prospective longline deployments were conducted in surrounding areas of the eastern section of Golfo Nuevo, as well as in San José and San Matías Gulf to the north (A Irigoyen unpubl. data 2025). The recorded CPUE values were 92.5% lower than those observed in the area during the high season and even lower than those of the low season, with a CPUE of 0.015 (captures hooks-1 h-1) (A Irigoyen unpubl. data 2025).

Further, in 2021 Baited Remote Underwater Video Station (BRUVS) surveys were undertaken with >400 deployments along the coast of the southwest Atlantic between 41–55°S, including several deployments within the area (n = 97) (P Merlo unpubl. data 2025). Despite the low visibility in the area during January, four BRUVS deployments recorded a MaxN (maximum number of individuals of a species observed in a single frame) of two individuals, and one deployment in the area recorded three individuals in the same frame (P Merlo unpubl. data 2025). Based on the maximum value of MaxN and the medium MaxN, Golfo Nuevo had a high relative abundance of Tope compared with the rest of the areas surveyed, suggesting that this area serves as an aggregation site for the species (Irigoyen et al. 2015; Jaureguizar et al. 2018; P Merlo unpubl. data 2025).

Historical data from commercial fisheries during February and April in 2001 reported a total of 319 Tope with full stomachs, including prey items such as Argentine Hake Merluccius hubbsi, Cuskeels Genypterus blacodes and Raneya brasiliensis, and squid Illex argentinus, with 90% of stomachs surveyed containing food (Elias et al. 2004). It is possible that Tope aggregate in this area to feed, but further information is required to confirm the nature and function of these aggregations.

SUBMIT A REQUEST

ISRA SPATIAL LAYER REQUEST

To make a request to download the ISRA Layer in either a GIS compatible Shapefile (.shp) or Google Earth compatible Keyhole Markup Language Zipped file (.kmz) please complete the following form. We will review your request and send the download details to you. We will endeavor to send you the requested files as soon as we can. However, please note that this is not an automated process, and before requests are responded to, they undergo internal review and authorization. As such, requests normally take 5–10 working days to process.

Should you have questions about the data or process, please do not hesitate to contact us.

    * indicates required

    Industry or sector (*)

    Under the terms and conditions of our User License Agreement , full and appropriate acknowledgement is required in any materials and publications derived from the data (and copies should be sent to the IUCN SSC Shark Specialist Group through the contact form). For any publications making substantial use of the data, the ISRA welcomes the opportunity for co-authorship, collaboration, and to comment prior to publication.


    Furthermore, we need to know whether you are a commercial or non-commercial user. Non-commercial includes scientific research, education or conservation. Commercial is defined as follows: any use by, on behalf of, or to inform or assist the activities of a commercial entity (that operates ‘for profit’) or use by a non-profit for the purposes of revenue generation

    Type of use(*):

    Please specify which layer (ex. all layers, layers within a specific Region, layers within a Jurisdiction or a single ISRA): Purpose (*):

    Please provide a description of how you intend to use the ISRA GIS Dataset. The more details you provide, the faster we can respond to your request. We may require further clarification prior to providing access. (min. 100 characters – max 1,000 characters)



    File format request (*)

    By providing your personal data, you consent to its processing as described below. The IUCN SSC Shark Specialist Group will use the information you provide on this form to send the documents you requested. You can change your mind at any time by writing to the ISRA Data Coordinator www.sharkrayareas.org/contact. All personal details provided will be treated with respect. For any information you can visit our Privacy Policy.
    Please read the User License Agreement and ISRA Layer Metadata Description

    This form uses Google reCaptcha to reduce spam. Privacy - Terms