Senegalese hake, Benguela hake - Mauritania, Senegal and Gambia|
Fact Sheet Title Fact Sheet |
| | Senegalese hake, Benguela hake - Mauritania, Senegal and Gambia |
Merlu noir (Merluccius senegalensis et Merluccius polli) - Mauritanie, Sénégal et Gambie; Black hake (Merluccius senegalensis and Merluccius polli) - Mauritania, Senegal and Gambia |
| Data Ownership | This document provided, maintained and owned by Food and Agriculture Organization (FAO) , is part of CECAF Stock Status Reports data collection. |
| ident Block | ident Block | | Species List: | Species Ref: en - Senegalese hake, fr - Merlu du Sénégal, es - Merluza del Senegal, ru - Мерлуза синегальская |
Species Ref Type: Measure Species Ref: en - Benguela hake, fr - Merlu d'Afrique tropicale, es - Merluza de Benguela, ru - Мерлуза бенгальская |
Species Ref Type: Measure |
|
| ident Block Senegalese hake, Benguela hake - Mauritania, Senegal and Gambia Aq Res Ident Aq Res Ident Aq Res Ident fao Sub Div |
---|
34.1.32 | Atlantic, East central / 34.1.32 |
---|
34.3.11 | Atlantic, East central / 34.3.11 |
---|
34.3.12 | Atlantic, East central / 34.3.12 |
---|
|
|
|
|
| Aq Res | Biological Stock: Biological Stock
Value: Regional Management Unit: Management Unit
Reference Year: 2012
|
Considered a management unit: An aquatic resource or fishery is
declared as [Fishery] Management Unit if it is
effectively the focus for the application of selected
management methods and measures, within the broader
framework of a management system. According to the FAO
Glossary for Responsible Fishing, "a Fishery Management
Unit (FMU) is a fishery or a portion of a fishery
identified in a Fishery Management Plan (FMP) relevant
to the FMP's management objectives." FMU's may be
organised around fisheries biological, geographic,
economic, technical, social or ecological dimensions ,
and the makeup and attribute of a fishery management
unit depends mainly on the FMP's management
objectives. |
Jurisdictional distribution: Jurisdictional qualifier (e.g.
"shared", "shared - highly migratory") of the aquatic
resource related with its spatial distribution. |
Environmental group: Classification of the aquatic
resource according to the environmental group (e.g.
pelagic invertebrate, or demersal fish) to which the
species belong. |
| | | | Aq Res State Trend Fcur/F0.1: Ratio between the observed fishing mortality coefficient during the last year of the series and F0.1. Fcur/FMSY: Ratio between the observed fishing mortality coefficient during the last year of the series and the coefficient that would give a maximum sustainable yield over the long term. Bcur/B0.1: Ratio between the estimated biomass for the last year and the biomass corresponding to F0.1. Bcur/BMSY: Ratio between the estimated biomass for the last year and the biomass corresponding to FMSY. Unless otherwise indicated, the indicators were based on the Schaefer dynamic production stock assessment model. Habitat Bio Climatic Zone: Tropical. Bottom Type: Soft bottom clean sand; Soft bottom muddy or muddy-sand. Depth Zone: Shelf 50 200m; Slope 200 1000m. Horizontal Dist: Neritic; Oceanic. Vertical Dist: Demersal. Geo Dist Geo Dist: Shared between nations Water Area Overview Spatial Scale: Spatial Scale Water Area Overview | Water Area Overview Senegalese hake, Benguela hake - Mauritania, Senegal and Gambia
fao Sub Div | 34.1.32: Atlantic, East central / 34.1.32 | 34.3.11: Atlantic, East central / 34.3.11 | 34.3.12: Atlantic, East central / 34.3.12 |
| | | | Water Area Overview
eez | MRT: Mauritania | SEN: Senegal | GMB: Gambia |
| | | | Water Area Overview |
Water Area OverviewSenegalese hake, Benguela hake - Mauritania, Senegal and Gambia Aq Res Struct Biological Stock: Biological Stock No detailed studies on black hake stock identity are available. The two black hake species are found in Moroccan, Mauritanian and Senegalese waters. The Senegalese hake (Merluccius senegalensis), found exclusively in the Eastern Central Atlantic, is caught between 33° N and 10° N, whereas the tropical African hake (Merluccius polli) is fished between 25° N and 18.5° S (Fernández et al., 2008; Lloris, et al., 2003). Due to their morphological resemblance and overlapping occurrence at certain depths, both species are mixed in catches and are commonly marketed as Merluccius spp. Stock assessment is therefore carried out as a single stock. Exploit Fishery Indicator Fishery Indicator | Fishery Indicator | Fishery Indicator | Fishery Indicator | Fishery Indicator |
---|
Type | Measure | 21033 | tonnes | 1983 | Measure | 15598 | tonnes | 1984 | Measure | 11558 | tonnes | 1985 | Measure | 12861 | tonnes | 1986 | Measure | 11960 | tonnes | 1987 | Measure | 11648 | tonnes | 1988 | Measure | 14534 | tonnes | 1989 | Measure | 13380 | tonnes | 1990 | Measure | 13464 | tonnes | 1991 | Measure | 20217 | tonnes | 1992 | Measure | 22606 | tonnes | 1993 | Measure | 16091 | tonnes | 1994 | Measure | 19037 | tonnes | 1995 | Measure | 16281 | tonnes | 1996 | Measure | 16795 | tonnes | 1997 | Measure | 18538 | tonnes | 1998 | Measure | 17080 | tonnes | 1999 | Measure | 15354 | tonnes | 2000 | Measure | 18150 | tonnes | 2001 | Measure | 17430 | tonnes | 2002 | Measure | 13624 | tonnes | 2003 | Measure | 12307 | tonnes | 2004 | Measure | 10238 | tonnes | 2005 | Measure | 8744 | tonnes | 2006 | Measure | 8300 | tonnes | 2007 | Measure | 8219 | tonnes | 2008 | Measure | 8363 | tonnes | 2009 | Measure | 6476 | tonnes | 2010 | Measure | 7763 | tonnes | 2011 | Measure | 6883 | tonnes | 2012 |
Bio Assess Assessment year: 2013 The CECAF Working Groups have adopted the following Biological Reference Points (BRPs): - Limit Reference points: BMSY and FMSY - Target Reference Points: B0.1 and F0.1 Stock status is assigned based on current estimates of fishing mortality (Fcur) and biomass (Bcur) relative to these target and limit reference points (Bcur/BMSY, Fcur/FMSY, Bcur/B0.1, Fcur/F0.1). The results from the stock assessment of this stock are found under the “Biological state and trend section”. Assess Models Type: Biomass-aggregated Schaefer dynamic production model For the assessments of black hake in Mauritania, total catch and abundance indices of Spanish trawlers targeting fresh hake were used. The CPUE series of this fleet was used as abundance index since it is the most complete and representative of the resource abundance. Although these data cover the whole period 1983-2012, the latest years from 2000 to 2012 are representative of the new fishing strategy period.Two assessment tests were carried out with the global model for the Mauritanian zone:<br/> - A first test with the total catch and CPUE abundance indices from 1983 to 2012. To fit this long data series to the models, the environmental effect was taken into account.<br/> - A second test with the latest total catch and CPUE abundance indices from 2000 to 2012, considering the most recent fishing strategy. No environmental effect was used. The parameters used were r= 0.50 per year, K=50 000 tonnes and BI/K=30 percent.<br/> Assess Models Type: Size-structured Length Cohort Analysis (LCA) Data on length structure collected by the IEO teams from landings of hake vessels in 1991–2012 were available. However, in view of several uncertainties about the middle of the series (this is explained in the 2010 WG), only the 2004-2012 data were used to run the LCA analytical model (see Section 2.4.3 of FAO 2016b). Yield per Recruit Analysis (Y/R) Sci Advice Taking into consideration the contradictory results of the assessments, the Working Group recommends obtaining information on the catches of black hake as bycatch from other fleets (retained and discarded) and their sizes through an observation programme. The current fishing effort should be increased by 10 percent, whilst waiting for confirmation on the state of the stocks. Management Management: Management Sources FAO. 2016a. Fishery Committee for the Eastern Central Atlantic, Report of the seventh session of the Scientific Sub-Committee, Tenerife, Spain, 14–16 October 2015 / Comité des pêches pour l’Atlantique Centre-Est Rapport de la septième session du Sous-Comité scientifique. Tenerife, Espagne 14-16 octobre 2015. FAO Fisheries and Aquaculture Report / FAO Rapport sur les pêches et l’aquaculture No. 1128. Rome, Italy. http://www.fao.org/3/I5301Bi/i5301bi.pdfFAO. 2016b. Report of the FAO/CECAF Working Group on the Assessment of Demersal Resources – Subgroup North. Fuengirola, Spain, 18–27 November 2013. / Rapport du Groupe de travail FAO/COPACE sur l’évaluation des ressources démersales – Sousgroupe Nord. Fuengirola, Espagne, 18-27 novembre 2013. CECAF/ECAF Series/COPACE/PACE Séries. No. 15/77. Rome, Italy/Italie. http://www.fao.org/3/a-i5114b.pdf |
|
| |
|
|