Eu data collection framework (dcf), reg. 199/2008, 665/2008 and decision 2008/949/EC


ANNEX IV- Coorperation Tropical Tunas



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ANNEX IV- Coorperation Tropical Tunas


IRD/IEO/AZTI cooperation under DCF for tropical tuna fleets

(2011-2013 period)

Context

The main characteristic of this fishery stems from the fact that virtually the entirety of the catches are obtained outside EU waters and transhipped at ports in neighbouring countries that have in most – but not all – cases signed fisheries agreements with the EU. For nearly 30 years, the responsibility for the collection of statistics on catches and the sampling of this European fleet segment has been shared between the IEO (Instituto Español de Oceanografía) and the IRD (Institut de Recherche pour le Développement), in close cooperation with the countries nearest these resources: Côte d’Ivoire and Senegal in the Atlantic, Seychelles and Madagascar in the Indian Ocean.

The sampling methodology used for tropical tuna fisheries sampling is that defined under the European ET project (“Analysis of the tropical tunas multi-species sampling scheme” no. 95/37, 1995-1997). Catches at sea are monitored through exhaustive logbook collection. They usually involve a small number of species and are stored directly in freezer wells containing brine without prior sorting, except for albacore tuna, or to discard certain non-commercial species. Sorting is carried out later on landing on the basis of commercial categories, these being more related to the weight of the individual fish than to their species. As a consequence, it is imperative to carry out sampling of the species composition of these landings in order to estimate the actual catches of each species as well as concurrently determining the demographic composition. The ET project involved an in-depth analysis of the sampling system (counting of species and measurement of length of albacores, bigeye and skipjack) and the processing of the data on catches in the Atlantic and Indian Oceans from 1991 to 1995.

Using these results, a new stratified sampling system was defined on the basis of simultaneous sampling of length and species and applying stratification based largely on the fishery mode (log sets or free school sets) and homogeneous spatial and temporal strata. The main consequence of this was the disappearance of the former “fleet segment” stratum which made a distinction between Spanish and French purse seiners, thus anticipating the current approach. As a result, the two research bodies involved (IEO for Spain and IRD for France) decided as early as 1998 to combine their efforts and carry out coordinated sampling of their fleet segments with a view to the best possible coverage of the defined strata. A detailed description of the procedures used was provided in the final report of the ET project, and also in the initial project submitted by France in 2002.

In june 2009, an international working group gathering scientists from the four tuna regional organization (ICCAT, CTOI, IATCC, WCPFC) was held in Sète (France) in order to compare the different multi specific sampling schemes used in the three oceans. The WG underlined in particular the necessity for the European fleet to re-analyse the sampling scheme in order to estimate bias and uncertainties associated with (i) well selection, (ii) the use of set in place of well as unit of sampling and (3) the use of sampling strata defined on data from the 90s whereas the fishery has changed since.

Cooperation under national programmes

Since 2000, collaborations between IEO and IRD on tropical tunas take the form of coordination meetings carried out every year alternatively in France and in Spain. In 2003 AZTI starts joining the group and participates regularly since 2007 to the annual meeting particularly for observer programs. Where the monitoring of tuna fishing fleets is concerned, such grouping of the resources available to the three research bodies is relevant at a number of levels:



  • Data on length, species composition and biology: shared funding of joint sampling teams in the main ports where catches are landed (Victoria, Seychelles; Abidjan, Côte d’Ivoire; Dakar, Senegal), coordinated for each ocean by French (IRD) and Spanish (Fisheries Directorate) technical staff;

  • Assessment of discards and bycatch: although the two programmes were conducted independently, the data collection protocols, the data input/verification applications, the central database and final data processing are all carried out jointly;

  • Development of common tools: the following were defined and developed jointly:

  • Sampling procedures and manuals (catches and length) and for collection of information by on-board observers (discards);

  • The data input/verification module for data on catches and samples (Avdth) along with observer data;

  • Processing modules for data on estimation of catches by species and by length (T3) and estimation of discards;

  • The definition and implementation of identical national databases in order to facilitate later processing (Balbaya, Sardara, Obstuna, etc.);

  • Final data processing common to both fleet segments: the chosen principle whereby all samples from both fleets are used entails an annual updating of the joint sample file for the processing of the data collected by the two organisations.

Details of cooperation for 2011-2013

- Discards

Each of the three organisations (IEO, AZTI for Spain and IRD for France) is in charge of its own observer programme; the manuals and data input/verification modules have been developed jointly and final processing of the data is done for both fleet segments without any particular financial impact. A common database and acquisition tool have been developed facilitating data sharing and common analysis.

Acknowledging the difficulty in embarking observers on tuna vessels since 2009 due to piracy in the Indian Ocean, the three institutes will collaborate during the period in a feasibility study searching for alternate solutions to observers like auto sampling and electronic monitoring.

- Landing ages and length

Generally speaking, the sampling systems are coordinated, executed and funded jointly. The activities are monitored in the field or remotely by Spanish and IRD technical staff in Victoria (Seychelles) and Dakar (Senegal), Abidjan (Côte D’Ivoire), Antsiranana (Madagascar) along with IRD and IEO researchers based in Sète and the Canaries Centre, who provide overall monitoring for the Atlantic and Indian Oceans.

The tasks entailed by this activity are carried out in conjunction with local research bodies in the following locations:


  • Atlantic:

  • Abidjan, Côte d'Ivoire (CRO, Centre de Recherches Océanologiques d’Abidjan).

  • Dakar, Senegal (ISRA/CRODT, Centre de Recherches Océanographiques de Dakar-Thiaroye).

  • Potentially, Tema (Ghana).

  • Indian:

  • Victoria, Seychelles (SFA – Seychelles Fishing Authority)

  • Madagascar (USTA, Unité Statistique Thonière d'Antsiranana / Antsiranana tuna statistics unit)

  • Port Louis, Mauritius (Albion Fisheries Center)

The sampling system had been created to reflect the seasonality of this fishery, but changes in the latter might involve adjustments to the system.

In 2010-2012 period, an analysis of the sampling scheme in place will be done in common with the following objectives:



  • Analysis of the spatial and temporal variability of statistical data from recent available period (1980-2008) and form super-sampling operation conducted in 2008 in the Indian Ocean,

  • Potential adjustment of sampling scheme on port and on board and during data computation taking into account logistical constraints (i.e. unloading duration) and associated costs (financial and human resources, sampling duration),

  • Estimation of accuracy of data produced within DCF.

- Other biological parameters

These are collected in the canneries context applying the same framework and conditions as for length sampling at the point of landing with independent funding and using existing survey teams.

- Access to data and coordination

Coordination meeting for actions conducted by IRD and IEO are carried out every year (and with AZTI since 2007), alternatively in France and Spain. These help define the partners’ respective frameworks for field actions, in addition to decisions on desirable changes in the various common applications and databases, and the definition of joint processing of the data to be carried out, and, lastly the preparation and allocation of the work to be done in the context of statutory ICCAT and IOTC meetings.

Implementation of the databases is planned independently in the national programmes, with developments being conducted in a context of mutual consultation.

Madrid, March 4th 2010

Pierre Chavance, IRD DCF tropical tuna programme coordinator

Alicia Delgado de Molina, IEO Canarias DCF tropical tuna programme coordinator

Iñaki Artetxe, AZTI DCF programme coordinator.

  1. ANNEX V- CECAF métier descriptions


SPANISH CEPHALOPOD FISHERY

RCM

RCM LDF (Long Distance Fisheries)

Name of métier:

OTB_CEP_>=70_0_0

Flag countries:

ESP

Date of update:

31- 12- 2009

Description of the métier

Spatial distribution of the fishing activity of the métier

Territorial waters of Mauritania and Guinea Bissau
Mauritania: Coastal, shelf and slope. Mauritania, North Cap Timiris (19º15.6’N), out of the protected area delimited in the Fishery Agreement and South Cap Timiris, beyond 6 miles.
Guinea Bissau: shelf and slope. Guinea Bissau, Beyond 12 nautical miles from the base line including the Guinea-Bissau/Senegal joint management area, extending north to the azimuth 268°.


Seasonal pattern of the fishing activity of the métier

The fleet is operative all the year, excepting during those months of close season. Some vessels share licences in both countries, moving from one to the other fishing ground, especially during the Mauritanian close season.

Number of vessels involved in metier by LOA group (Appendix III EC949/2008):

31 (24<40 m)




Detailed gear types and selectivity devices used in métier

Bottom otter trawl

Management measures

Mauritania:

Closed area: Out of the fishing area established by the Agreement, North of latitude 19° 15,6’ N, outside the zone marked by the following points:

  • - 20° 46,3’ N 17° 03,0’ W

  • - 20° 40,0’ N 17° 07,5’ W

  • - 19° 57,0’ N 17° 07,5’ W

  • - 19° 28,2’ N 16° 48,0’ W

  • - 19° 18,5’ N 16° 48,0’ W

  • - 19° 18,5’ N 16° 40,5’ W

  • - 19° 15,6’ N 16° 38,0’ W

South of latitude 19° 15,6’ N as far as latitude 17° 50,0’ N, west of 9

miles from the 6-mile line, the coordinates.



Authorised gear Bottom trawl. Doubling of the cod-end and Doubling of the twine forming the cod-end are prohibited.

Minimum authorised mesh size: 70 mm

Biological recovery

Two periods of two months: May-June and September-October.



By-catches: 5 % shrimps

Minimum sizes:

Octopus vulgaris 500 g (eviscerated); Loligo vulgaris 13 cm and Sepia

officinalis 13 cm

Authorised tonnage: 13 950 GT per licence period.

Guinea Bissau:

Fishing zone: Beyond 12 nautical miles from the base line, including the Guinea-Bissau/Senegal joint management area, extending north to the azimuth 268°.

Authorised gear: Standard otter trawls and other selective gear are authorised. Outriggers are authorised. In the case of all fishing gear, no methods or devices may be used to seek to obstruct the mesh of the nets or reduce their selective effect. Doubling of the codend’s netting yarn, whether single or multiple, shall be prohibited.

Minimum authorised mesh size: 70 mm

By-catches: Cephalopod trawlers may not hold on board crustaceans accounting for more than 9 % of their total catch in Guinea-Bissau’s fishing zone at the end of a trip.

Authorised tonnage: 1 421 authorized tonnage (GT) per year.

Main target and by-catch species for the métier

Target species: Octopus (Octopus vulgaris), Cuttlefish (Sepia hierredda, S.officinalis) and Squid (Loligo vulgaris)

By-catch species: M. senegalensis, M. polli, Solea spp. and Dentex spp.











Indicate level of discard of major species (mostly subset of G1 or G2 species)

Species

Level of discarding










DISCARD DATA NOT AVAILABLE







Is significant part of the catches landed in foreign countries?


Landing country

Sampling agreement (y/n)




Until 2008 mainly vessels landed in Gran Canaria, Canary Islands. Nowadays, most of the landings takes place at Nouadhibou Port (Mauritania) and are carried afterwards to Gran Canaria by freighter. In other cases, it is port of Vigo (Galicia, NW Spain) that is used for landings.

NO


Sampling of the metier

Indicate if this Métier is merged with other metiers for sampling

NO

Justification for merging:




Sampling scheme

Type of sampling

The sampling scheme will be on-board (scheme 1), provided that on-board observers are present.



Sampling frame and primary sampling unit for data collection

One trip per quarter will be sampled, as the fishing trips are of long duration, always more than 2 weeks (from 1 to 3 months)

Data collected

Retained catch and discarded catch.



Concurrent at market and Concurrent at sea (provided that on-board observers are present)

Observers at sea

NO




Self sampling

NO




Sampling landings on shore

Samples purchase on market.




Indicate if the Métier is associated with particular sampling problems:

The fishing sector is reluctant to put observers on-board so until now all the biological data have been obtained from purchased samples. Therefore this samples purchase system will be maintained and the on-board concurrent sampling will not be possible until the shipowners allow observers on-board.

It is essential to realise that, in most cases, the possibility of sampling the selected metiers will depend, as has been explained, on the possibility of having observers on board the vessels in question. In this connection, it should be remembered that, in spite of the efforts made in previous years, observers have only been able to board the hake fleet. In view of the new requirements, there is great concern about this matter, since, without the sector’s collaboration on this point, it would not be possible to carry out any concurrent sampling by metier as required by the new regulation.

In the late years, assistance have been provided by the staff hired by the SGM in Mauritania, which is collaborating with the IEO staff in the biological sampling of fresh material landed in Nouadhibou (Mauritania). This task have been suspended from October 2009.


Additional remarks (historical and others):

The number of vessels has decreased during last years, there are only about 23 active vessels now (roughly 55 active vessel in 1999).

Sampling dependent on the existence of and possibility of access to the fishery. Stocks shared with fleets of coastal and non-Community countries so that the fisheries in the CECAF area are dependent on the fishing agreements between the EU and this countries.





INDUSTRIAL CRUSTACEAN FISHERY

RCM

RCM Long Distance Fisheries

Name of métier:

OTB_CRU_>=40_0_0

Flag countries:

ESP

Date of update:

31- 12- 2009

Description of the métier

Spatial distribution of the fishing activity of the métier

Territorial waters of Mauritania


Mauritania: Coastal, shelf and slope. Mauritania, North Cap Timiris (19º15.6’N), out of the protected area delimited in the Fishery Agreement and South Cap Timiris, beyond 6 miles.

Guinea Bissau: shelf and slope. Guinea Bissau, Beyond 12 nautical miles from the base line, including the Guinea-Bissau/Senegal joint management area, extending north to the azimuth 268°.



Seasonal pattern of the fishing activity of the métier

The fleet is operative all the year, excepting during those months of close season. Some vessels share licences in both countries, moving from one to the other fishing ground, especially during the Mauritanian close season.

In Mauritania, the seasonal pattern is very clear: fleet targets mainly Parapenaeus longirostris during the first six months of the year. During the summer the fishery especially targets Farfantepenaeus notialis, as it occurs in November and December, after the close season (Sepetembre-October).



Number of vessels involved in metier by LOA group (Appendix III EC949/2008):

36 (24-<40) (2008)




Detailed gear types and selectivity devices used in métier

Gear type: bottom otter trawl. These shrimpers usually alternate the use of outriggers and the classic bottom otter trawl with trawl doors (“baka” type), depending on the target species. Thus, outriggers are used to fish P. longirostris and F. notialis, while the classic bottom otter trawl with trawl doors is employed for a deeper fishery, especially targeting A. varidens and C. maritae.

Management measures

Mauritania:

Closed area: Out of the fishing area established by the Agreement:

- North of latitude 19° 21,0’ N, outside the zone marked by the following points:



  • 20° 46,30’ N 17° 03,00’ W

  • 20° 40,00’ N 17° 07,50’ W

  • 20° 05,00’ N 17° 07,50’ W

  • 19° 35,50’ N 16° 47,00’ W

  • 19° 28,00’ N 16° 45,00’ W

  • 19° 21,00’ N 16° 45,00’ W

-South of latitude 19° 21,0’ N, west of the six-mile line.

Closed season: Two periods: May-June and September-October.

Gear-related measures: Minimum mesh size: 50 mm. Doubling of the cod-end prohibited. Doubling of the twine forming the cod-end prohibited. Protective aprons are authorised in accordance with Article 24 of the Mauritanian Fisheries Code

Aquatic species-related measures: minimum sizes and weights of the saltwater fish, cephalopods and crustaceans established by the Fishing Agreement. Limitation of by-catches: 20% fish, 15% cephalopods and 7,5 % crabs. Prohibition of catches of spiny lobster.

Effort control: 7 313 GT authorized tonnage (GT) per licence period.

Guinea Bissau:

Closed area: Out of the fishing area established by the Agreement (Beyond 12 nautical miles from the base line, including the Guinea-Bissau/Senegal joint management area, extending north to the azimuth 268°.



Gear-related measures: Minimum mesh size: 40 mm. Doubling of the cod-end’s netting yarn, whether single or multiple, prohibited. Methods or devices may be used to seek to obstruct the mesh of the nets or reduce their selective effect prohibited.

Aquatic species-related measures: Limitation of by-catches: 50 % of fishes and cephalopods by fishing trip.



Effort control: 1 421 authorized tonnage (GT) per year.


Main target and by-catch species for the métier

Target species: Deep-water pink shrimp (Parapenaeus longirostris) and Southern pink shrimp (Farfantepenaeus notialis)

By-catch species: Red shrimp (Aristeus varidens) and Crab (Chaceon

maritae)










Indicate level of discard of major species (mostly subset of G1 or G2 species)

Species

Level of discarding










DISCARD DATA NOT AVAILABLE







Is significant part of the catches landed in foreign countries?


Landing country

Sampling agreement (y/n)

Low % is landed in Noadhibou (Mauritania), but the mainly catches are transferred to merchant vessels and transported to the port of Huelva (Spain).

NO


Sampling of the metier

Indicate if this Métier is merged with other metiers for sampling

NO

Justification for merging:




Sampling scheme

Type of sampling

The sampling scheme will be on-board (scheme 1).



Sampling frame and primary sampling unit for data collection (trip, day etc etc)

One trip per quarter will be sampled, as the fishing trips are of long duration, always more than 2 weeks (from 1 to 3 months)

Data collected

Retained catch and discarded catch.



Concurrent-at-sea

Observers at sea

YES

Self sampling

NO




Sampling landings on shore

Until 2008, Samples purchase on market. For 2009 (see below)




Indicate if the Métier is associated with particular sampling problems:

During the period 2003-2008, and into the framework of the National Data Collection Programme of the EU, biological and length samplings were carried out by the IEO. Shrimp samples from Mauritanian catches were obtained from freezer shrimp enterprises located at Huelva, through the collaboration of the National Association of Crustacean Freezer Shrimpers Shipowners (ANAMAR). Furthermore, in November 2007, the personnel of the Spanish fisheries office in Nouadhibou, started to collaborate with the IEO in sampling fresh shrimps supplied by the Spanish shrimpers that fished in waters off Mauritania. However, due to several problems in obtaining these samples, this collaboration was intermittent and unfortunately was finally ceased when the Fisheries Office was closed in October 2009.

The failures in the sampling system carried out until the moment (lack of samples of all the needed categories every month), the need of carrying out discards studies and the new type of concurrent sampling established in the new Regulation of the Community Program, have involved the development of important changes in the sampling strategy. This sampling strategy is necessary based on the periodical work of scientific observers on-board the shrimpers vessels operating in waters of the Mauritania. Finally, and after some years of hard efforts made by the IEO to achieve it, the Spanish shrimpers’ fleet has allowed having observers on board since January 2010.



Additional remarks (historical and others):


Sampling dependent on the existence of and possibility of access to the fishery. Stocks shared with fleets of coastal and non-Community countries so that the fisheries in the CECAF area are dependent on the fishing agreements between the EU and this countries.



HAKE TRAWL FISHERY

RCM

RCM Long Distance Fisheries

Name of métier:

OTB_DEF_>=70_0_0

Flag countries:

ESP

Date of update:

31- 12- 2009

Description of the métier

Spatial distribution of the fishing activity of the métier

Territorial waters of Mauritania and Morocco.

Seasonal pattern of the fishing activity of the métier

The fleet is operative all the year.

Number of vessels involved in metier by LOA group (Appendix III EC949/2008):

9 (24<40 m)


Detailed gear types and selectivity devices used in métier

Bottom otter trawl for hake

Management measures

Mauritania:

Fishing zone:

North of latitude 19° 15′ 60″ N, west of the line joining the following

points:


  • 20° 46′ 30″ N 17° 03′ 00″ W

  • 20° 36′ 00″ N 17° 11′ 00″ W

  • 20° 36′ 00″ N 17° 36′ 00″ W

  • 20° 03′ 00″ N 17° 36′ 00″ W

  • 19° 45′ 70″ N 17° 03′ 00″ W

  • 19° 29′ 00″ N 16° 51′ 50″ W

  • 19° 15′ 60″ N 16° 51′ 50″ W

  • 19° 15′ 60″ N 16° 49′ 60″ W

South of latitude 19° 15′ 60″ N as far as latitude 17° 50′ 00″ N, west of the 18-mile line from the low-water mark.

South of latitude 17° 50′ 00″ N, west of the 12-mile line from the low-water mark.

The zone to the north of latitude 19°15,60’ N is more restricted during the biological recovery of cephalopod. (for coordinates see DO L 203 31 July 2008).



Authorised gear: bottom trawl.

Doubling of the cod-end is prohibited.

Doubling of the twine forming the cod-end is prohibited.

Minimum authorised mesh: 70 mm for the trawl net.

Authorised tonnage: 3 240 GT for Spain and per licence period.

The zone to the north of latitude 19°15,60’ N is more restricted during the biological recovery of cephalopod. (for coordinates see DO L 203

31 July 2008).

By-catches: 25% Fish

Prohibited catches: Cephalopods and crustaceans.

Minimum sizes: Hake (Merluccius spp.) 30 cm.

Morocco:

Fishing zone: south of latitude 29ºN a depth of more than 200 m.

No vessels authorised: 22 vessels (maximum of 11 trawlers per year)

Type of vessel: Average size of 275 GT,

Geographical limit: South of 29º N. Beyond the 200 m isobath

The biological recovery period is that fixed for cephalopods.

Authorised net trawling: net of min. 70 mm.

Doubling of the cod-end is prohibited.

Doubling of the twine forming the cod-end is prohibited.

By-catches:0 % of cephalopods and crustaceans, with the exception of crab (5 %)


Main target and by-catch species for the métier

Targed species: Black hakes (Merluccius polli and M. senegalensis); European hake: M. merluccius (very occasionally in Morocco).

by-catch species: anglerfish (Lophius vaillantii), silvery John Dory (Zenopsis conchifer), redfish (Helicolenus dactylopterus) and various elasmobranch species (Centrophorus granulosus, C. squamosus, Raja spp.










Indicate level of discard of major species (mostly subset of G1 or G2 species)

Species

Level of discarding

Merluccius spp.

Significant (> 10% in weight)

(average 15 %, varies widely)






Is significant part of the catches landed in foreign countries?

Landing country

Sampling agreement (y/n)

Landing requirement 50 % of catches made in Morocco (DO L 141/2006)

NO

Sampling of the metier

Indicate if this Métier is merged with other metiers for sampling

NO

Justification for merging:




Sampling scheme

Type of sampling

The sampling scheme will be on-board concurrent sampling (scheme 1), provided that on-board observers are present.



Sampling frame and primary sampling unit for data collection

One fishing trip per month will be sampled, as fishing trips lasting less than two weeks.

Data collected

Retained catch and discarded catch.



Concurrent-at-sea

Observers at sea

YES




Self sampling

NO




Sampling landings on shore

NO (only samples separates on-board by the observer)




Indicate if the Métier is associated with particular sampling problems:

Acute difficulties due to the lack of availability of some of the logbooks from 2008 (75%) and the closing of the fishing Bureau (Noadhibou). Absolute lack of information from Morocco. Both issues increase the need for the aforementioned documents.

Additional remarks (historical and others):


Increasing dwindle of the vessels. Some of the boats now refuses to let observers in. As a consequence, the foreseen ratio (one trip per month) is not attainable.

Sampling dependent on the existence of and possibility of access to the fishery. Stocks shared with fleets of coastal and non-Community countries so that the fisheries in the CECAF area are dependent on the fishing agreements between the EU and this countries.





SPANISH SMALL PELAGIC FISHERY

RCM

RCM Long Distance Fisheries

Name of métier:

PS_SPF_0_0_0

Flag countries:

ESP

Date of update:

31- 12- 2009

Description of the métier

Spatial distribution of the fishing activity of the métier

Territorial waters of Morocco

Shelf, beyond 2 miles, North of 34º18’N.



Seasonal pattern of the fishing activity of the métier

The fleet dynamics varies through the year. During the period 1988-1999, the higher effort of the fleet targeting anchovy was carried out along the third quarter (maximum average value of 186 fishing trips in September). This main fishing season in Moroccan waters occurs just after the main one in the Gulf of Cadiz (spring-summer) (Ramos and Millán, 2006). The fishing strategy deployed in 2007 has showed some differences because of some punctual circumstances occurring during this year. In this way, higher fishing effort in Moroccan waters was applied in May, followed by a sharp decrease the following month and a second peak in July and August. From September onwards, the effort progressively decreased, one month before than in the series 1988-1999 (García-Isarch, et al., 2008).

Number of vessels involved in metier by LOA group (Appendix III EC949/2008):

19 (18-<24 m)



Detailed gear types and selectivity devices used in métier

The gear is locally called “traiña”. The main body-net is composed of a number of long and rectangular sheet nets, horizontally delimited thought all its length by resistant net strips. The net is vertically kept through a lead-line in the ground-rope and a buoyed line in the head-rope. The purse line, locally called “jareta”, closes the seine when the fish school is surrounded, forming a big bag with the catches inside. They used to attract the schools by using powerful lights, that increased the fishing efficiency (not allowed in the last fishing Agreement).


Management measures

Maximum authorised dimensions of the seine net: 500 m × 90 m.

Ban on fishing with “lampara” nets.



Access control: Vessel size < 100 GT.

Number of licensed vessels: 20

Closed area: out of the area North of 34º18’N and beyond 2 miles

Closed season: Two months: February and March.

Main target and by-catch species for the métier

Target species: European anchovy (Engraulis encrasicolus)

Associated species: European sardine (Sardina pilchardus)-20%; scomber mackerels (Scomber spp), jack and horse mackerels (Trachurus spp)-5%










Indicate level of discard of major species (mostly subset of G1 or G2 species):

Species

Level of discarding










No significant (> 10%)








Is significant part of the catches landed in foreign countries?



Landing country

Sampling agreement (y/n)

Morocco

Landing requirements established by the last Fishery Agreement, (2006):

First year: 25 %; second year: 30 %; third year: 40 %; fourth year: 50 %.

NO


Sampling of the metier

Indicate if this Métier is merged with other metiers for sampling

NO

Justification for merging:




Sampling scheme

Type of sampling

Sampling scheme 1 will be applied, since, as the catch is largely of one species, it is considered that complete sampling of all the species can be carried out in the wholesale market.



Sampling frame and primary sampling unit for data collection

One fishing trip per month will be sampled, as these vessels carry out daily fishing trips.

Data collected

Retained catch.



Concurrent at market


Observers at sea

NO




Self sampling

NO




Sampling landings on shore

Landing samples will also be bought in order to carry out biological parameter sampling.




Indicate if the Métier is associated with particular sampling problems:

Sampling dependent on the existence of and possibility of access to the fishery. Stocks shared with fleets of coastal and non-Community countries so that the fisheries in the CECAF area are dependent on the fishing agreements between the EU and this countries.

Monthly sampling in the wholesale market of the purse seine metier fishing in Morocco will also provide good coverage, given that it is a small fleet (maximum 20 purse seiners) that makes landings at only one port (Barbate).



Additional remarks (historical and others):


More restrictive fishery conditions of this metier since the last Fishery Agreement (2006) in relation to the ones before the closure of the fishery in 1999.

In 2007, there was a much lower level of effort and far fewer landings were made than in the years prior to the end of the agreement in 1999 (around 12000 t in 1998, 1999). Therefore, and in the hope that this metier will in the future acquire the significance, and the social and economic importance, that it had previously, it has been selected for commencement of sampling.




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