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The IUCN/SSC Shark Specialist Group

Shark News 14: March 2002

The artisanal ray fishery in the Gulf of California: development, fisheries research and management issues
J. Fernando Márquez-Farias, Instituto Nacional de la Pesca, México
Introduction
Fishing for rays in the Mexican Pacific developed with the introduction of bottom gillnets in the Upper Gulf of California, where local fishers target flounder, grouper, and many other finfish resources. The boats used for fishing rays are typical "pangas" 22-25ft in length, using outboard motors and operated by 1-3 fishers. Fishing trips are from 1- 3 days in duration, and the operation depth varies with the target group of species. The number of boats used in the ray fishery is currently unknown but is assumed to be high. Fishers tend to switch to ray fisheries depending on the availability of other resources, for example during seasons when more valued resources such as blue crab, shrimps and sierra are restricted due to regulatory regimes. The catch is processed on the beach and stored in ice trucks.

The distribution is mostly regional and includes fresh fillets or salt dried meat. The quality is judged primarily on the colour of the meat (i.e. darker colour = less value). In general, as with other artisanal fisheries in México, the ray fishery is characterized by limited infrastructure for processing, low technology, limited fishing ratio, income supplies and marketing controlled by few companies or middlemen, and an unarticulated role with respect to regional economies.

Figure 1. Average proportion of rays production by Mexican Pacific states. Dark shaded states represent the Gulf of California region.
figure 1


The fishery for rays extends along the Gulf of California on both sides of Peninsula de Baja California to the Southern Mexican Pacific Coast. The importance of the ray fishery in terms of production decreases from North to South (Figure 1).

Compared to the shark fishery that dates back to the late 1930's, the catch of rays in México is a fairly new activity. The documentation of production began officially in 1986, assuming previously unregistered catches. The peak catch of rays was 1996 with 6,666t, and in 2000 the catch had decreased to 4,944t. The average catch for all Mexican Pacific states during the period from 1990 to 2000 was 5,514t, showing a relative stable trend. Catch production of the Gulf of California surrounding states represented 93% of the Pacific Coast total production during the same period (Figure 2).

Figure 2. Annual catches of rays in the Pacific Ocean.
figure 2


Species composition
Despite the development of the ray fishery, very few specific studies have been conducted in the Gulf of California region. Most have been carried out along the South West Coast of Baja California, Bahía Almejas and provide limited information. This, however, represents the only information produced regarding some commercially important rays in the region (R. productus, R. steindachneri, G. marmorata, N. entemedor, among others), which, unfortunately is mostly published in low impact journals. Undoubtedly the most valuable survey on rays and sharks in the Gulf of California was carried out in a twoyear multi institutional research project conducted during 1998-99, lead by Dr. Robert Hueter from CSR/ MML (Status of the shark and ray fishery resources in the Gulf of California: Applied Research to Improve Management and Conservation. Email: rhueter@mote.org).

A multispecies complex structure and a wide spectrum of life history strategies of the elasmobranchs studied were elucidated as a result of the biological examination of the catch in this survey. Species registered in Sonora state alone show the high diversity and relative importance in the catches (Table 1). The first five species represent almost 90% of the catches. Species composition varied depending mainly on the gillnet mesh size used and the season.

Table 1. Relative proportion of rays in Sonora.
Species

%

Rhinobatus productus 37.98
Dasyatis brevis 18.95
Rhinoptera steindachneri 14.45
Gymnura marmorata 10.94
Narcine entemedor 5.00
Rhinobatus glaucostigma 4.40
Gymnura crebripuncata 2.74
Myliobatis californica 2.21
Zapterix exasperata 1.61
Raja velezi 1.24
Urobatis maculatus 0.18
Dasyatis longus 0.07
Mobula munkiana 0.06
Urotrygon chilensis 0.05
Mobula japanica 0.04
Myliobatis longirostris 0.03
Urotrygon rogersi 0.02
Urobatis halleri 0.01


Bycatch
Rays have been caught traditionally as bycatch in well-developed fisheries such as: blue crab (Callinectes bellicosus), sierra (Scomberomorus sierra and S. concolor), and shrimp (Litopenaeus spp., and Farfantepenaeus spp.). A gross calculation of the level of bycatch in the shrimp fishery using a 1:10 bycatch ratio (1 kg/ shrimp:10 kg/bycatch biomass) (Garcia-Caudillo et al. 2000), indicated the excessive biomass of rays that have been caught in the Gulf of California during the last 60 years. This prompted us to speculate that ray mortality level from bycatch exceeds the mortality level from the directed ray fishery in the Gulf of California. Parallel commercial activity has developed as a consequence of the large amounts of rays caught in the shrimp trawlers. This informal activity, consisting of middlemen buying the bycatch from the shrimp trawlers, is resulting in disadvantageous competition for the authentic fishermen, mainly because the price of the product from the trawlers is low due to the low operational costs. In addition, rays are frequently caught in traps used in the blue crab fishery and in gillnets used for sierra.

The research
From almost no knowledge about the ray catches in the Gulf of California in 1998, basic information on the fishery, biology and life history styles of several commercially important rays is now recognized. Specifically, the research priorities of Instituto Nacional de la Pesca (INP) and preliminary results are:

  • Fishing gear selectivity. Because the fishing gears are constructed based on the fishers' experience, their characteristics and dimensions inevitably vary. Panels of different mesh size can be used and various types of net. Catch performance of gillnets in terms of selectivity is currently being examined. As expected, preliminary results have indicated different impacts on the population depending on the size selectivity properties of gillnets.

  • Embryonic growth. Monitoring pregnant females in the catch is used to estimate the season of parturition and the relative area of pupping grounds in Sonora state. Synchronization between embryonic growth of several species of rays and average surface temperature of the Gulf of California has been found.

  • Fecundity. The number of pups produced by species demonstrates the wide range of litter sizes. Some species are recognized as highly productive such as Rhinobatos spp. (3-10 pups), and Gymnura marmorata (2-15 pups). Contrarily, species such as Rhinoptera steindachneri (1 pup) and Mobula (1 pup) have an extraordinary low fecundity.

  • Maturity. Macroscopic sexual organs and histological surveys of shell glands and testes for several species are examined from specimens to investigate the possibility of sperm storage as a reproductive strategy, and for validation of the size at maturity. The maturity stages of the species are being compared to the selectivity of gillnets in order to estimate the trend of the gear to retain juveniles.


Regulation and management issues
Shark management in México is still in the process of implementation due to radical opposition by the recreational sector demanding the inclusion of allowable proportions of billfishes as bycatch by longliners and drift gillnet vessels. A summary of regulation guidelines for the shark fishery was described by Castillo et al. (1998). Regulation of the shark fishery also includes measures for rays. Unfortunately, the main causes retarding the implementation of the regulations for sharks are of political order going beyond the facilities of the INP, and currently, the commercial ray fishery is not regulated.

However, through the INP, a new instrument for fisheries management has been developed, the Carta Nacional Pesquera, CNP (National Fisheries Chart). The CNP has legal and obligatory status and brings encouraging possibilities to incorporate the scientific findings of a particular fishery resource (either a single species or a group of species) identified as a Fishing Management Unit (FMU). This management tool will allow INP to build a record summarizing the state of knowledge of a specific FMU which could be implemented and updated annually. Anyone who is able to contribute to the knowledge of a certain resource can incorporate information via the Internet (http://inp.semarnap.gob.mx/ convocatoria/). This information is then reviewed and refereed by a panel of experts. In this way, information on ray resources has already been submitted and is currently undergoing the review process. Ironically, regulation of rays in the Gulf of California could be implemented faster than the Federal Management Plan for sharks (which includes ray-like species), which has been in the planning and development stages for at least seven years.

Legally protected elasmobranch species in Mexico Manta rays Manta birostris, Mobula japanica and Mobula lucasana have been protected since March 25, 1994 in the 12 miles perimeter surrounding the Revillagigedo archipelago (Isla San Benedicto, I. Clarion, Roca partida, I. Socorro and I. Guadalupe) in the Mexican Pacific. Commercial fishing is legal in other areas (Camhi et al., in prep).

References
Camhi, M. et al. Global Status of Sharks. In preparation. Occasional Paper of the IUCN Species Survival Commission. IUCN/SSC Shark Specialist Group. IUCN, Gland, Switzerland.

Castillo-Geniz, J. L., J. F. Márquez-Farias, M. C. Rodríguez de la Cruz, E. Cortés and A. Cid del Prado. 1998. The Mexican artisanal shark fishery in the Gulf of Mexico: towards a regulated fishery. Mar. Freshwater Res. 49:611-20.

Garcia-Caudillo, J. M., M. A. Cisneros-Mata and A. Balmori. 2000. Performance of a bycatch reduction device in the shrimp fishery of the Gulf of California, Mexico. Biological Conservation 92:199-205.

J.Fernando Márquez-Farias
Instituto Nacional de la Pesca. Programa Tiburón.
Centro Regional de Investigación Pesquera, Calle 20 Sur,
605. CP 85400 Guaymas, Sonora, México.
Fax: (622) 22- 2-59-25
Email: fmarquez@tetakawi.net.mx