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| Marine Resource Fact Sheet |
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| Orange roughy - South East Atlantic |
| | Data Ownership | | This document provided, maintained and owned by South East Atlantic Fisheries Organisation (SEAFO) , is part of SEAFO Stock Status Reports data collection. |
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| Related observations | Locate in inventory | | | | Species: | | FAO Names: en - Orange roughy, fr - Hoplostète orange, es - Reloj anaranjado, ru - Большеголов атлантический (=берикс исландский) |
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| Geographic extent of Orange roughy - South East Atlantic Map tips - Click on
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| FAO Fishing Statistical Division Areas |
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| 47.A.0 | SEAFO division A.0 |
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| 47.A.1 | SEAFO division A.1 |
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| 47.B.0 | SEAFO division B.0 |
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| 47.B.1 | SEAFO division B.1 |
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| 47.C.0 | SEAFO division C.0 |
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| 47.C.1 | SEAFO division C.1 |
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| 47.D.0 | SEAFO division D.0 |
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| 47.D.1 | SEAFO division D.1 |
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| Main Descriptors | Considered a single stock: Yes Spatial Scale: Regional
Management unit: Yes Reference year: 2019
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| Considered a single stock: A group of individuals in a species occupying a well defined spatial range independent of other stocks of the same species. It can be affected by random dispersal movements and directed migrations due to seasonal or reproductive activity. |
| Spatial Scale: Spatial scale contains a standard term such as Global, Regional (e.g. for the whole Atlantic), sub-regional (e.g. for a part of the Atlantic), national, local (for sub-national levels). |
| 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. |
| Reference Year: The Reference Year is the last year considered in the stock assessment and/or fishery status. |
| | | | | | Biological State and Trend History Exploration for Orange roughy in the SE Atlantic first started in South Africa prior to 1994, but the focus soon shifted to Namibia when an exploratory fishing license was given to a Namibian fishing company to search for commercial deep-water fish species. The fishery expanded, extending their fishing range into SEAFO CA in 1995. By 2008, a three-year moratorium on Orange roughy was enforced in Namibia and the fishery has not been re-opened yet. There are however some targeted fishing activities as part of the research quota allocated to the vessel that conducts the scientific survey in Namibia. Table 1 shows vessels that operated between 1995 and 2005 in the SEAFO CA. These vessels were also involved in the Alfonsino fishery during the same period. Seven Namibian vessels (Table 1) were involved for the period that the fishery occurred in the SEAFO CA, between 1995 and 2005. These vessels were also involved in the Alfonsino fishery during the same period. The vessels employed the standard New Zealand “Arrow” rough bottom trawl with cut-away lower wings. Sweep and bridle lengths were 100 meters and 50 meters respectively. A “rock hopper” bobbin rig was used. The net had a 5-6-meter headline height when towed at 3- 3.5 knots and had an estimated wingspread of 15 meters. The cod end had a mesh of 110 mm. Each vessel spends on average 12 days at sea. Table 1. Orange roughy: Fleet information, Division B1. | Flag | ID | Name | Length | GRT | Built | HP | IRCS | | Nam | L737 | Southern Aquarius | 54 | | 01/01/1974 | 3000 | V5SH | | Nam | L913 | Emanguluko | 31 | 483.00 | 01/01/1990 | 1850 | V5SD | | Nam | L892 | Petersen | 43 | 650.00 | 01/01/1979 | | V5RG | | Nam | L861 | Will Watch | 69 | 1587.00 | 01/01/1972 | 2116 | ZMWW | | Nam | L918 | Hurinis | 37 | 784.00 | 01/01/1987 | 1680 | V5SW | | Nam | L1159 | Bell Ocean II | 57 | 1899.00 | 01/01/1990 | 3342 | 3BLG | | Nam | L830 | Seaflower | 92 | 3179.75 | 01/01/1972 | 4800 | V5HO | Habitat and Biology Climatic zone: Temperate. Bottom type: Unspecified. Depth zone: Slope (200 m - 1000 m). Horizontal distribution: Oceanic. Vertical distribution: Demersal/Benthic. The aggregating behaviour of Orange roughy contributed to its vulnerability to overexploitation globally. Spawning aggregations of Orange roughy have been targeted in Namibia during winter. Outside the spawning seasons catches were found to be lower due to a more dispersed resource. Orange roughy are also extremely slow-growing and estimates of maximum age are in excess of 100 years. Recruitment to the fishery is poorly understood as juveniles are not found in significant quantities. Adults have been caught in small amounts in both Angolan and South African waters, but not in large spawning aggregations as in Namibia. Orange roughy distribution also extends beyond the economic zones of the BCLME countries with good catches reported for example on the Valdivia Bank on the South Atlantic Ridge as well as on the fringes of the Agulhas Bank and Walvis Ridge in the southern Benguela. Orange roughy ( Hoplostethus atlanticus) is distributed globally (Fig. 1), but predominantly in the Southern Hemisphere.  | Figure 1. Global distribution of Orange roughy (Branch 2001).  |
Geographical Distribution Jurisdictional distribution: Straddling between High Seas and EEZ Fishing mainly occurred on Ewing seamount and Valdivia Bank within the SEAFO CA. These operations started in 1995 and continued until 2005, with the exception of 1998 when no fishing took place. The fishing season usually extends from January to December and catches peak in winter months (May to July), which coincides with the spawning season of Orange roughy.  | | Figure 2. Geographical location of fishing activities in the SEAFO CA. |
Geo References  | | Geographic extent of Orange roughy - South East Atlantic
| FAO Fishing Statistical Division Areas | 47.A.0: SEAFO division A.0 | | 47.A.1: SEAFO division A.1 | | 47.B.0: SEAFO division B.0 | | 47.B.1: SEAFO division B.1 | | 47.C.0: SEAFO division C.0 | | 47.C.1: SEAFO division C.1 | | 47.D.0: SEAFO division D.0 | | 47.D.1: SEAFO division D.1 |
| | | | | | Intersecting Major FAO areas and LME areas |
The following area codes have been found as intersecting the distribution of Orange roughy - South East Atlantic Resource Structure Considered a single stock: Yes In the SE Atlantic Orange roughy may most probably be regarded as a single stock (management unit). In the BCLME region that species occurs within the economic zones of each of the coastal states as well as in the SEAFO CA. Exploitation For all the fishing grounds the home port is the same as the landing port, with Walvis Bay and Lüderitz the most important ports. All available landing information is presented in Table 2. However, the bulk of Orange roughy catches were recorded within the Namibian EEZ (Table 3). A total of 1270 trawls were made landing about 290 tonnes of Orange roughy. Table 2. Catches of Orange roughy made by Namibia, Norway and RSA. | Nation | Namibia | Norway | South Africa | | Fishing method | Bottom trawl | Bottom trawl | Bottom trawl | | Management Area | B1 | A1 | B1 | | Catch details (t) | Retained | Discarded | Retained | Discarded | Retained | Discarded | | 1995 | 40 | | N/F | | | | | 1996 | 8 | | N/F | | | | | 1997 | 5 | | 22 | | 27#** | | | 1998 | N/F | N/F | 12 | | | | | 1999 | <1 | | N/F | N/F | | | | 2000 | 75 | | 0 | | | | | 2001 | 94 | | N/F | N/F | | | | 2002 | 9 | | N/F | N/F | | | | 2003 | 27 | | N/F | N/F | | | | 2004 | 15 | | N/F | N/F | | | | 2005 | 18 | | N/F | N/F | | | | 2006 | N/F | N/F | N/F | N/F | | | | 2007 | N/F | N/F | N/F | N/F | N/F | N/F | | 2008 | N/F | N/F | N/F | N/F | N/F | N/F | | 2009 | N/F | N/F | N/F | N/F | N/F | N/F | | 2010 | N/F | N/F | N/F | N/F | N/F | N/F | | 2011 | N/F | N/F | N/F | N/F | N/F | N/F | | 2012 | N/F | N/F | N/F | N/F | N/F | N/F | | 2013 | N/F | N/F | N/F | N/F | N/F | N/F | | 2014 | N/F | N/F | N/F | N/F | N/F | N/F | | 2015 | N/F | N/F | N/F | N/F | N/F | N/F | | 2016 | N/F | N/F | N/F | N/F | N/F | N/F | | 2017 | N/F | N/F | N/F | N/F | N/F | N/F | | 2018 | N/F | N/F | N/F | N/F | N/F | N/F | | 2019 | N/F | N/F | N/F | N/F | N/F | N/F | N/F = No Fishing. Blank fields = No data available. ** Sum of Catches from 1993 to 1997. # Values taken from the Japp (1999). Table 3. Orange roughy landings (tonnes) in SEAFO CA and Namibian EEZ. | Year | SEAFO CA | Namibian EEZ | | 1994 | N/F | 1 872 | | 1995 | 40 | 6 288 | | 1996 | 8 | 17 381 | | 1997 | 5 | 14 729 | | 1998 | N/F | 10 040 | | 1999 | <1 | 2 699 | | 2000 | 75 | 1 344 | | 2001 | 94 | 874 | | 2002 | 9 | 1 985 | | 2003 | 27 | 1 730 | | 2004 | 15 | 1 106 | | 2005 | 18 | 297 | | 2006 | N/F | 429 | | 2007 | N/F | 288 | | 2008 | N/F | 6 | | 2009 | N/F | 5 | | 2010 | N/F | 1 | | 2011 | N/F | 1 | | 2012 | N/F | 2 | | 2013 | N/F | 2 | | 2014 | N/F | 1 | | 2015 | N/F | 6 | | 2016 | N/F | 236 | | 2017 | N/F | 113 | | 2018 | N/F | 433 | | 2019 | N/F | 226 | Assessment The annual CPUE (total annual catch divided by number of tows) are shown in Figure 3. Catch per tow was used as a proxy for CPUE estimations due to a lack of duration information. The CPUE was the highest in 1995 and thereafter decreased rapidly to reach the lowest CPUE in 1999. Since then the CPUE seems to have stabilized at a low level until 2005 after which there are no data.  | | Figure 3. CPUE of Orange roughy in tonnes per trawl in Division B1 (SEAFO SC Report 2006). |
Data Catch records for the period 1995 to 2005 are available (see Table 2 above). The number of hauls made per year are depicted in Table 4 and shows that more hauls were recorded in years when the catches were high. Deep-sea fish surveys were conducted in the SEAFO CA by the Spanish research vessel, Vizconde de Eza (2008 -2010) (Vizconde) and the Norwegian research vessel, Dr Fridtjof Nansen (2015 and 2019) (Nansen), under the FAO’s EAF-Nansen Programme. During 2015, the Nansen surveyed some seamounts, but only at the Ewing and Valdivia seamounts where evidence of Orange roughy presence discovered (Bergstad et al 2019). A trawl deployed on Valdivia north caught some Orange roughy (22 specimens) and camera dives at Ewing also detected Orange roughy. During the 2019 Nansen survey, no Orange roughy were detected in the surveyed area (Division D1). The findings of the 2015 survey could only determine the presence or spatial distribution, but not the abundance of Orange roughy in the surveyed areas. Table 4. The total number of sets from which Orange roughy catches were derived for the period 1995-2005. | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | | 20 | 223 | 188 | 0 | 16 | 327 | 295 | 40 | 63 | 46 | 61 | Overall Assessment Results Since there is no fishery in recent years or any other independent data available within the SEAFO CA, no assessment can be done at the moment. Scientific Advice SC considered available data on Orange roughy since the inception of the fisheries in SEAFO CA. There is no fishery data available since 2005 for Orange roughy within the SEAFO CA, as a result SC cannot conduct stock assessment of the Orange roughy stock within the Convention Area. The conservation measure 32/16 on the moratorium of a directed fishery for Orange roughy was discussed in detail during the 2018 SC meeting. Historically, most of the catches were made in Division B1. There is currently zero tonnes allocation (moratorium) with a 4 tonnes bycatch allowance in Division B1, 50 tonnes in the remainder of the SEAFO CA, subject to exploratory fishing protocols. Management Management unit: Yes Management Advice For 2021, the SC recommends that a research quota is set for a pre-planned research survey inside Division B1, to be conducted with a suitable commercial vessel. A task force has been established to draft a survey proposal to be presented to the Commission for approval. A harvest control rule shall be developed for Orange roughy in the future as data becomes available. The annual catch and set TAC outside the B1 are shown in Figure 4. There was no landing recorded since 2005.  | | Figure 4. Orange roughy catches and set TAC outside the B1 since 2005. |
Source of information SEAFO “SC-SEAFO-2016. Report of the 12th Annual Meeting of the SEAFO Scientific Committee. SEAFO SC Report 2016.” 2016  http://www.seafo.org/media/4ca98f5f-c111-4bcf-875b-36ac3213b8b7/SEAFOweb/pdf/SC/open/eng/SC%20Report%202016_pdf Bibliography Boyer, D.C., C.H. Kirchner, M.K. McAllister, A. Staby and B.I. Staalesen “The Orange Roughy Fishery of Namibia: Lessons to be learned about managing a developing Fishery. South African Journal of Marine Science, 23, 205-221.” 2001. Branch, T.A. “A Review of Orange Roughy (Hoplostethus atlanticus) Fisheries, Estimation Methods, Biology and Stock Structure. Payne, A. I. L., S.C. Pillar & R.J.M. Crawford, eds. A Decade of Namibian Fisheries Science. South African Journal of Marine Science. 23:181 - 203.” 2001. Anon “Social economic studies. Deepfishman. Case Study 1A Report. Namibian Orange Roghy. Institute of Economics Studies. University of Iceland.” 2010. Anon “Capricon Fisheries Monitoring. State of Stock Review Report No. 2. In: Japp D.W., M.G. Purves and S. Wilkinson, Status of the Fishery Resources in the Benguela Current Large Marine Ecosystem. Cape Town.” 2011. Anon “Ministry of Fisheries and Marine Resources. State of the Resource TAC recommendations report; Orange roughy. Namibia.” 2008. |
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