Volutid snails as an alternative resource for artisanal fisheries in northern patagonic gulfs: availability and first suggestions for diving catches.
Snails, Edible (Distribution)
Fish industry (Management)
Environmental sustainability (Research)
Ciocco, Nestor F.
|Publication:||Name: Journal of Shellfish Research Publisher: National Shellfisheries Association, Inc. Audience: Academic Format: Magazine/Journal Subject: Biological sciences; Zoology and wildlife conservation Copyright: COPYRIGHT 2008 National Shellfisheries Association, Inc. ISSN: 0730-8000|
|Issue:||Date: April, 2008 Source Volume: 27 Source Issue: 2|
|Topic:||Event Code: 200 Management dynamics; 310 Science & research; 690 Goods & services distribution Advertising Code: 59 Channels of Distribution Computer Subject: Company distribution practices; Company business management|
|Product:||Product Code: 0900000 Fishing, Hunting & Trapping NAICS Code: 114 Fishing, Hunting and Trapping SIC Code: 0912 Finfish; 0913 Shellfish; 0921 Fish hatcheries and preserves|
|Geographic:||Geographic Scope: Argentina Geographic Name: Patagonia Geographic Code: 3ARGE Argentina|
ABSTRACT Volutid snails have been identified as a potential
resource for artisanal fisheries in northern patagonic gulfs. We
explored their availability in two gulfs of Chubut Province (Patagonia,
Argentina) by means of SCUBA diving and baited traps. CPUE and biomass
were estimated from visual counting densities. CPUE of all the volutes
was 65.85 kg x [diver.sup.-1] x [h.sup.-1] and 59.5 kg x [diver.sup.-1]
x [h.sup.-1] in San Matias (SMG) and San Jorge (SJG) Gulfs,
respectively. Estimated biomass was 89.7 ([+ or -] 28.9) and 44.4 ([+ or
-] 19.2) tons in SMG and SJG. The species Adelomelon ancilla and
Odontocymbiola magellanica could supplement the potential clam fishery
existent at SJG. In SMG Zidona followed by O. magellanica could be the
main commercial target. We suggest minimum catch sizes of 16 cm for Z.
dufresnei, 9 cm for O. magellanica, and 12 cm for A. ancilla. Protection
of the egg capsules and females would help the protection of the
resource. These measures could ensure the sustainability of a
small-scale multispecific fishery.
KEY WORDS: edible snails, diving fisheries, artisanal resources, north Patagonia
Gastropods of the Volutidae family have been identified as a potential resource for artisanal diving and trawling fisheries in north patagonic gulfs (Ciocco 1995, Ciocco 1999) and for the semi-industrial trawling fleet centered in Mar del Plata (north coast of Argentina) (Lasta et al. 1998). The most common volutid species in Argentinean coasts are: Zidona dufresnei (Donovan, 1832), Odontocymbiola magellanica (Gmelin, 1791), Adelomelon ancilla (Solander, 1786), Adelomelon brasiliana (Lamarck, 1811) and Adelomelon beckii (Broderip, 1836). The only commercially exploited species recorded until now is Z. dufresnei from Mar del Plata coasts, with landings of up to 1,700 tons in 1997 (Lasta et al. 1998, Gimenez et al. 2005). In the gulfs of northern Patagonia, the catches of the "tehuelche scallop" Aequipecten tehuelchus (d'Orbigny, 1846) are considered the only mollusc fisheries of significance for local economies (Ciocco et al. 2006). In the case of volutid snails, regular commercial landings are still infrequent in Patagonian coasts, with the exception of sporadic small catches. However, in other regions of the world marine gastropods are starting to be incorporated as new fishery resources because of their high economic value. This can lead to overexploitation and, because of the biological fragility of this kind of resource, to the collapse of the fisheries in some cases (Tegner 1989, Castilla 1996, Hobday et al. 2001). The study of reproductive cycles and population dynamics of fisheries resources is necessary when stating management policies. In the last years reproductive biology of Argentinean volutids have been studied (Gimenez & Penchaszadeh 2002, Gimenez & Penchaszadeh 2003, Miloslavich et al. 2003, Cledon et al. 2005a, Bigatti 2005; Arrighetti & Penchaszadeh 2006, Bigatti et al. in press) as well as ecology and longevity of some species (Gimenez et al. 2004, Cledon et al. 2005b, Bigatti et al. 2007). Some of these species are present in northern patagonic gulfs, so the previous knowledge achieved must be taken into account when assessing the sustainability of the fisheries of these potential resources.
In this study we explore the availability of volutid snails in the coasts of Chubut Province (Patagonia, Argentina) and suggest the first management rules for potential diving artisanal fisheries targeting this resource.
MATERIALS AND METHODS
To detect areas with volutids availability compatible with commercial shellfish catches, prospecting surveys in the southwest of the San Matias (SMG) and the San Jorge (SJG) Gulfs were performed (Fig. 1). Studied area in SMG was delimitated from Puerto Lobos (42[degrees]00'S, 65[degrees]04'W) and the region comprised between Barranca Blanca and Punta Quiroga (42[degrees]13'S; 64[degrees]40'W); in SJG sampling was done between Punta Castillos (65[degrees]56'W) and Punta San Roque (65[degrees]39'W). A total of 32 transects were performed in SJG and 29 in SMG (Fig. 1). Those were defined between 2-5 to 20-25 m depth, perpendicularly to the line coast, each 1' (latitude = 1,800 m; longitude [[approximately equal to] 1,200 m), or fraction (30" or 15") according to coast line characteristics. Observations were made by a SCUBA diver that was "trawled" using a boat at a speed of 3 to 5 km [h.sup.-1]. Each transect included 150-m length semitransects, in which the diver counted and registered underwater the number of snails observed in a band wide of 1 m. Stock assessment estimations were carried out from the number of snails recorded at each transect using equations to estimate total N and associated standard error from surveys data in simple random sampling following Thompson (1999). Mean individual wet weight by gulf (all captured individuals from different species grouped) was assigned to the estimated total N to calculate total biomass. Additionally, in SJG experimental catches using snail traps with bait were done; 5 to 20 traps were anchored at different depths for 3 to 6 h. In the transects with higher snail densities and commercial possibilities, CPUE was estimated by a diver fishing snails by hand during 5 min, and extrapolating results to kg [diver.sup.-1] [hour.sup.-1]. Shell length (precision: 0.1 mm) and wet weight (precision: 0.1 g) of all snails caught during the CPUE sampling were registered. For the species O. magellanica and A. ancilla foot performance weight percentage was calculated as: (foot wet mass/total wet mass) x 100. In the case of Z. dufresnei we use the foot performance reported by Gimenez et al. (2005).
[FIGURE 1 OMITTED]
On the other hand a survey between fishermen and restaurant owners was performed to assess the sale price of snails in the zone.
San Matias Gulf (SMG)
A total of 158 semitransects were done, prospecting 23,700 [m.sup.2] by direct visual counting (Fig. 1A). The following species were registered (Fig. 2A): Zidona dufresnei (65.2% of total snails registered), Odontocymbiola magellanica (24.6%), Adelomelon beckii (8.7%), and Adelomelon ancilla (1.4%). In the oriental zone (from Barranca Blanca to Pta. Quiroga area) the volutids density (all the species together) was up to 0.2 ind. [m.sup.-2], whereas the biomass oscillated between 50-80 g [m.sup.-2]. For Z. dufresnei the estimated CPUE ranged between 33-110 Kg [diver.sup.-1] [h.sup.-1], with specimens of more than 200 mm in shell length and a mean individual weight of 500 g. In only one case (transect 27, located near the east end of the explored area) a CPUE of 65.85 Kg [diver.sup.-1] [h.sup.-1] was recorded for the group of A. beckii, A. ancilla, and Z. dufresnei (Fig. 2D). The biggest individual of A. beckii captured weighed 3,175 g with a shell length of 365 mm. Estimated total N in the SMG surveyed area (equivalent to 30.9 [Km.sup.2]) was 150,066 ([+ or -]46,485) individuals, representing in general terms a mean of 0.5 snails/100 [m.sup.2] and a biomass of 89.7 ([+ or -]28.9) tons (Table 1).
San Jorge Gulf (SJG)
A total of 192 semitransects were performed by direct visual counting, covering an area of 28,800 [m.sup.2]. At the same time 65 snail baited traps were submerged. Relevant concentrations of A. ancilla (64% of total snails counted) and O. magellanica (36%; Fig. 2B) were detected in Bahia Huevo and Bahia Cayetano, with maximum densities of 0.2-0.3 ind. [m.sup.-2], whereas the snail biomass ranged from 45-65 g [m.sup.-2]. In Bahia Cayetano, medium shell length for A. ancilla was 147 mm (SD = 20.8; n = 16) and for O. magellanica 151 mm (SD = 9.9; n = 9). Medium individual weight for both species together was 285.32 g (SD = 60.85; n = 11). The estimated CPUE for both species together oscillated between 29-89 Kg [diver.sup.-1] [hr.sup.-1], and the mean for the species group was 59.5 Kg [diver.sup.-1] [hr.sup.-1] (Fig. 2D). No volutids were caught in the 65 snail baited traps. Estimated total N in the SJG surveyed area (equivalent to 16.6 [Km.sup.2]) was 155,550 ([+ or -]66,752) individuals, representing a mean of 0.9 snails/100 [m.sup.2] and 44.4 ([+ or -]19.2) tons of volutid biomass (Table 1).
Foot Performance and Commercialization
The muscular foot weight (used for human consumption) represents around 40% to 45% of the total weight for O. magellanica and A. ancilla (Fig. 2C) in both gulfs.
In the Chubut Province there has not been massive commercialization of volutid snails until present. Consumption is restricted to local restaurants and families. The sale price of O. magellanica reported by artisanal fishermen in Riacho San Jose (San Jose Gulf, approximately 100 Km south from SMG) is around 0.30 US dollars per unit, which gives a mean of 6.50 US dollars per Kg of fresh foot meat (without the shell) or 4 US dollars per Kg (entire animal) when sold to restaurants or locally consumers.
Marine snails represents approximately 2% of the molluscs global catches, and several gastropod genera such as Haliotis, Concholepas, Strombus, and Busycon show high economic values in international markets and play substantial roles in small scale artisanal fisheries (Leiva & Castilla 2002). In the north patagonic gulfs, marine snails are still captured occasionally and are consumed locally. In Argentina and Uruguay, Z. dufresnei occurring in the fishing area common to both countries, has been exploited for the last 30 y (Gimenez et al. 2005). The mean price of Z. dufresnei in the Argentinean internal market is 2-2.5 US dollars/Kg (Ciocco 1999). The sale price of O. magellanica (4 US dollars/Kg) for local consumption reported in this work is quite similar to that of Z. dufresnei. On the other hand, overall growth performance (OGP) of Z. dufresnei and O. magellanica is within the range of other commercial snails from temperate regions (Cledon et al. 2005b, Bigatti et al. 2007), which would make profitable its commercialization.
According to the registered abundances, the snails that could be commercially exploited in the SMG would be mainly Z. dufresnei followed by O. magellanica. Performances observed in the catches of Z. dufresnei set this resource as a support of a novelty fishery in the zone between Barranca Blanca and Punta Quiroga, area where 88.4% of the total volutid biomass estimated from SMG is concentrated, which results in around 79 tons of Z. dufresnei. Although individuals of A. beckii bigger than 3 Kg of total weight were registered in the zone, the observed densities are low, suggesting that the fishing of this species would not be profitable. Even though volutids present high sizes and somatic production, their slow growth rate, their late sexual maturity, and direct development lacking a free swimming larvae stage make this group extremely vulnerable to overexploitation (Bigatti et al. 2007), which would result in the loss of an important link in the trophic webs of the shallow waters benthic communities from north Patagonia.
The foot of Z. dufresnei represents 60% of the total body weight and is the only portion that is consumed (Gimenez et al. 2005), whereas the foot of O. magellanica and A. ancilla representing approximately 40% to 45% of the total body weight. Although the performance is higher in Z. dufresnei, fishing of all these species could be done alternatively, allowing the sustainable growing of the populations. In the SMG the CPUE value for the group of all the volutes was 65.85 kg [diver.sup.-1] [h.sup.-1] (A. beckii, A. ancilla, and Z. dufresnei), whereas in the SJG the CPUE was 59.5 kg [diver.sup.-1] [h.sup.-1] (A. ancilla and O. magellanica). Taking into account that the mean yield of all the species is around 50%, it could be obtained a mean CPUE of fresh meat of 32 kg [diver.sup.-1] [h.sup.-1]. In the SJG A. ancilla and O. magellanica could be a complementary target of a potential clam fisheries in the zone. By means of seasonal alternation of target species [the "red octopus," Enteroctopus megalocyathus (Gould, 1852), and infralitoral bivalves as the hard shell clam Protothaca antiqua (King and Broderip, 1832)] the local availability of resources could support a multispecific small scale fishery.
The fact that no snails were caught in the baited traps in SJG could be related to the feeding mechanism of the Volutidae family in the norpatagonic gulfs. O. magellanica feeds mainly on live molluscs that are previously narcotized by means of a salivary liquid produced by the predator salivary and accessory salivary glands; the feeding on carrion was registered at a low rate (Bigatti 2005).
Gimenez et al. (2005) propose a minimum capture size of 16 cm for Z. dufresnei on the coasts of Mar del Plata (north coast of Argentina) taking into account the first maturity size: 15 cm for males and 15.7 cm for females. These sizes correspond to individuals of 8 and 9 y old respectively (Gimenez et al. 2004). In this study, no data about reproductive season are available in the SMG, but the minimum size proposed by Gimenez et al. (2005) could be used as a parameter for the fisheries of Z. dufresnei in the Chubut province. Further studies about reproductive seasons of this species are recommended, because latitudinal (and environmental) variations lead to changes in reproductive physiology. First maturity size for O. magellanica in Nuevo Gulf (Chubut Province) is 80 mm for males and 90 mm for females (Bigatti et al. in press), corresponding to 7 and 8 y-old individuals respectively (Bigatti et al. 2007). Females lay egg capsules from July to December and embryos complete their development in 2-3 mo (Bigatti 2005). The modal wet weight of the animals is 62.8 g, reaching an age of up to 20 y; maximum individual somatic production is 29.3 g [yr.sup.-1] at a size of 145 mm (12 y old), and decrease thereafter (Bigatti et al. 2007). In the case of A. ancilla no aging studies were performed until now, but the minimum size of females observed laying egg capsules in the field is 114 mm and the minimum size of individuals analyzed with developed gonads is 102 mm in Nuevo Gulf. The main oviposition season is from June to November and intracapsular development takes approximately 3 mo in the same zone (Penchaszadeh et al. 2006).
Regarding the reproductive studies available for the species, we propose a minimum catch size of 16 cm for Z. dufresnei, 9 cm for O magellanica, and 12 cm for A. ancilla. Fisheries of A. beckii are not recommended because of the lack of reproductive and ecological studies of this species in the coasts of Chubut province and for the low density registered in the present work.
Volutid juveniles or immature individuals live mainly buried in the substratum (Bigatti 2005), which could protect them from the capture of artisanal diving fishermen or by trawling nets with mesh sizes exceeding the minimum catch sizes proposed in this paper. For the diving fisheries, instructing fishermen to discriminate between sexes by the pedal gland observation in volutid females (Aycaguer 2002, Bigatti 2005), as well as the protection of the egg capsules and females found, would help to protect the resource. In all the cases, when fished volutids are in the reproductive season, the capture of females should be avoided. These policies, together with a seasonal alternation of target species of other shellfish could support a small-scale multispecific fishery (Ciocco 1999), which would assure the stocks of artisanal volutid fisheries in the coasts of the north patagonic gulfs.
The authors thank the valuables comments and corrections on the manuscript made by J.M. Lobo Orensanz. Norberto de Garin and Guido Pastorino helped with maps and Mariana Lozada corrected the English version. The authors also thank Luis de Francesco for information about commercialization and Miguel A. Diaz, Ricardo Vera and Julio Rua for their help in field sampling.
Arrighetti, F. & P. E. Penchaszadeh. 2006. Ciclo reproductivo del caracol gigante Adelomelon beckii (Caenogasteropoda, Volutidae). VI Jornadas Nacionales de Ciencias del Mar. Puerto Madryn, Argentina, Abstracts Book. pp. 107.
Aycaguer, C. 2002. Anatomia de las volutas del Atlantico Sudoccidental, I: Anatomia general y del sistema reproductor de Zidona dufresnei (Donovan, 1823) (Neogastropoda: Volutidae). Com. Soc. Malac. Urug. 76-77:159-180.
Bigatti, G. 2005. Anatomia, ecologia y reproduccion del caracol rojo Odontocymbiola magellanica (Gastropoda: Volutidae) en golfos norpatagonicos. PhD. thesis. Universidad de Buenos Aires, Argentina. 178 pp.
Bigatti, G., P. E. Penchaszadeh & M. Cledon. 2007. Age, growth and somatic production in the volutid gastropod Odontocymbiola magellanica from Golfo Nuevo, Patagonia Argentina. Mar. Biol. 150:1199-1204.
Bigatti, G., E. M. Marzinelli & P. E. Penchaszadeh. Seasonal reproduction and sexual maturity of Odontocymbiola magellanica (Neogastropoda: Volutidae) in Patagonian shallow waters, Argentina. Invertebr. Biol. (in press).
Castilla, J. C. 1996. La futura red chilena de parques y reserves marinas y los conceptos de conservacion, preservacion y manejo en la legislacion nacional. Rev. Chil. Hist. Nat. 69:253-270.
Ciocco, N. F. 1995. La marisqueria mediante buceo en el golfo San Jose (Chubut, Argentina). Serie: Inf. Tecnicos del Plan de Manejo Integrado de la Zona Costera Patagonica. GEF-PNUD-FPN 2. pp. 1-39.
Ciocco, N. F. 1999. Relevamiento y sistematizacion de informacion sobre mariscos de interes para la pesca artesanal en las costas de Chubut. Consejo Federal de Inversiones-Pcia. del Chubut. Technical Report. 278 pp.
Ciocco, N. F., M. L. Lasta, M. Narvarte, C. Bremec, E. Bogazzi, J. Valero & J. M. Orensanz. 2006. Scallops fisheries in Argentina. In: S. Shumway & G. Parsons, editor. Developments in aquaculture and fisheries sciences. Scallops: biology, ecology, and aquaculture. ISBN 0444504826. Amsterdam: Elsevier Publ. Co. pp. 125l-1292.
Cledon, M., W. Arntz & P. E. Penchaszadeh. 2005a. Gonadal cycle in an Adelomelon brasiliana (Neogastropoda: Volutidae) population of Buenos Aires province, Argentina. Mar. Biol. 147:439-445.
Cledon, M., T. Brey, P. E. Penchaszadeh & W. Arntz. 2005b. Individual growth and somatic production in Adelomelon brasiliana (Gastropoda; Volutidae) off Argentina. Mar. Biol. 147:447-452.
Gimenez, J. & P. E. Penchaszadeh. 2002. Reproductive cycle of Zidona dufresnei. Mar. Biol. 140:755-761.
Gimenez, J. & P. E. Penchaszadeh. 2003. Size and sexual maturity in Zidona dufresnei (Caenogastropoda: Volutidae) of the southwestern Atlantic Ocean (Mar del Plata, Argentina). J. Mar. Biol. Ass. UK. 83:293-296.
Gimenez, J., T. Brey & P. E. Penchaszadeh. 2004. Age, growth and mortality of the prosobranch Zidona dufresnei (Donovan, 1823) in the Mar del Plata area, south-western Atlantic Ocean. Mar. Biol. 145:707-712.
Gimenez, J., M. Lasta, G. Bigatti & P. E. Penchaszadeh. 2005. Exploitation of the volute snail Zidona dufresnei (Donovan, 1823) in Argentine waters, South western Atlantic ocean. J. Shellfish Res. 24:1135-1140.
Hobday, A. J., M. J. Tegner & P. L. Haaker. 2001. Overexploitation of a broadcast spawning marine invertebrate: decline of the white abalone. Rev. Fish Biol. Fish. 10:493-514.
Lasta, M. L., N. F. Ciocco, C. S. Bremec & A. M. Roux. 1998. Moluscos Bivalvos y Gasteropodos. In: E. Boschi, editor. El Mar Argentino y sus recursos pesqueros. Los moluscos de interes pesquero. Cultivos y estrategias reproductivas de bivalvos y equinoideos. INIDEP, Mar del Plata 2. pp. 115-142.
Leiva, G. E. & J. C. Castilla. 2002. A review of the world marine gastropod fishery: evolution of catches, management and the Chilean experience. Rev. Fish Biol. Fish. 11:283-300.
Miloslavich, P., C. J. M. Sanchez-Antelo & P. E. Penchaszadeh. 2003. Desarrollo embrionario y contenido proteico del liquido intracapsular de Adelomelon ancilla (Lightfood, 1786) (Caenogatropoda: Volutidae). V jornadas Nacionales de Ciencias del Mar, Mar del Palta. Diciembre 2003.
Penchaszadeh, P. E., C. J. M. Sanchez-Antelo & G. Bigatti. 2006. Reproduccion y dieta del caracol Adelomelon ancilla en aguas someras del Golfo Nuevo. VI Jornadas Nacionales de Ciencias del Mar, 4 al 8 de Diciembre de 2006. Puerto Madryn, Argentina. Abstracts Book. 289 pp.
Tegner, M. J. 1989. The California abalone fishery: production, ecological interactions, and prospects for the future. In: J. F. Caddy, editor. Marine invertebrate fisheries: their assessment and management. New York: John Wiley and Sons. pp. 401-420.
Thompson, S. K. 1999. Sampling. New York: J. Wiley & Sons Inc. 343 pp.
GREGORIO BIGATTI * AND NESTOR F. CIOCCO
Centro Nacional Patagonico CENPAT-CONICET. Blvd. Brown 2825.U9120ACV. Puerto Madryn, Chubut, Argentina
* Corresponding author. E-mail: email@example.com
TABLE 1. Volutid stock assessment. Total Biomass Gulf N (tons) SMG 150,066 ([+ or -] 46,485.4) 89.7 ([+ or -] 28.9) SJG 155,550 ([+ or -] 66,752.4) 44.4 ([+ or -] 19.2) Mean Surveyed Weight Area Gulf (S) ([Km.sup.2]) SMG 597.6 ([+ or -] 53.9) 30.9 SJG 285.3 ([+ or -] 18,3) 16.6 SMG = San Matias Gulf; SJG = San Jorge Gulf; standard error between parenthesis. Mean weight corresponding to SMG was estimated from 69 snails (45 Z. dufresnei; 17 O. magellanica; 6 A. beckii; 1 A. ancilla), and Mean weight from the SJG estimated from 11 snails (7 A. ancilla; 4 O. magellanica). Figure 2. (A) Percentage of species sampled in SMG; (B) percentage of species sampled in SJG; (C) foot performance (% of foot weight from total weight); (D) CPUE for all the species together in SMG and sJG. San Matias Gulf species Zidona dufresnei 63.5, 64% Odontocymbiola magallanica 26.4, 26% Adalomelon beckii 8.7, 9% Adalomelon ancilla 1.4, 1% San Jorge Gulf species Odontocymbiola magallanica 64, 64% Adelomelon ancilla 36, 36% [GRAPHIC OMITTED] Note: Table made from bar graph.
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