Printer Friendly

Density and population parameters of sea cucumber Isostichopus badionotus (Echinodermata: Stichopodidae) at Sisal, Yucatan.


Sea cucumber represents an important fishery resource around the world since they have provided food and economic resources to small-scale fisherman for centuries (Conand, 1997). In many regions, they have been widely exploited for traditional food and medicinal purposes, which has led to a rapid decline of their natural populations, mainly in the Indo-Pacific, the traditional fishing grounds. This fact has led to the implementation of new fishing areas, where sea cucumbers are not consumed nor fished traditionally, such as the Galapagos Islands in Ecuador, Baja California in the Mexican Pacific and recently Yucatan in the Gulf of Mexico (Bruckner et al., 2003; Bruckner, 2006; Conand, 2017).

In Mexico, the sea cucumber catch began in 1980, in shallow waters of the Baja California coast, and the fishery was focused on the species Isostichopus fuscus (Reyes-Bonilla & Herrero-Perezrul, 2003). This species has received some research attention (FajardoLeon & Velez-Barajas, 1996; Herrero-Perezrul et al., 1999; Reyes-Bonilla & Herrero-Perezrul, 2003), although in just a few years the resource showed a drastic decline in abundance, with no evidence of recovery, and the fishery has been permanently closed for eight years (Reyes-Bonilla & Herrero-Perezrul, 2003).

In Yucatan State, the sea cucumber is caught since 2006, with the purpose of offering an alternative to fishermen during the ban of other resources (octopus, lobster, and fishes) and to optimize the seafood processing facilities in Sisal Harbor. In 2011, the Mexican government authorized permits to cooperative fishermen to catch sea cucumber for three months (February, April and May), although this fishing period has varied every year (DOF, 2011; Poot-Salazar et al., 2015; Hernandez-Flores et al., 2015). Approximately 1,080 ton was legally caught in 2011, although there are some reports of the same amount of illegal catch increasing in the area (Diario de Yucatan, 2011). In fact, there is not enough information about the density, biology, and ecology of the species fished to allow the design of management plans for a sustainable exploitation. Research on sea cucumbers is scarce for the Yucatan Peninsula; Fuente-Betancourt et al. (2001) evaluated the potential fishery in the Mexican Caribbean. In the Gulf of Mexico, Zetina-Moguel et al. (2003) mentioned three species as the most important by their size and abundance to the fishery. These species were distributed along the Yucatan coast in waters 20-30 m deep, apparently with a geographic segregation: Astichopus multifidus, more abundant in the Campeche coast, Isostichopus badionotus, and Holothuria floridana more abundant at Yucatan coast. In 2007, Rodriguez-Gil (2007) described the potential of the fishery and mentioned the same species distributed along the Yucatan coast, whereas LopezRocha (2011) evaluated the weight-length relationship and assessed population density in Sisal, recently, other studies have been realized in Yucatan coast (Hernandez-Flores et al., 2015; Poot-Salazar et al., 2015). There are no other specific reports about biomass evaluation or population dynamics that offer information for a sustainable use of the resource. Therefore, the aims of this study were: 1) to determine sea cucumber density in the fishing area, and 2) to offer information related to the population parameters in order to understand the species biology.


Study area

Sisal is located on the north-east coast of the Yucatan State, in the Gulf of Mexico. The fishing area is located up to 25 km off the coastline at 10-30 m deep (21[degrees]00'-21[degrees]30'N, 90[degrees]00'-90[degrees]30'W), data were collected in 10 samplings sites: S1 to S10 (Fig. 1). The sea floor is mainly covered with Thalassia testudinum, Syringodium filiforme, and macroalgae. Climate is warm and arid with rains in summer and a high percentage of rain in winter, [BS.sub.o] (h') w (x') according with Koppen climatic classification; the mean water temperature is 29[degrees]C, and the area is dominated by the Lazo Current (Delgado-Carranza et al., 2011).

Sea cucumber identification

Sea cucumber taxonomy was based on the presence of calcareous forms, such as the shapes and combination of microscopic spicules that are part of skeletal components in the body wall (Hickman, 1998). These spicules have different shapes, such as towers, rosettes, C-shaped, rods, buttons, and plates, and they are species specific. For I. badionotus the calcareous spicules are typically towered with 12 or 14 terminal spines, C-shaped structures bigger than basal disk in towers, and big rods, a complete key is described by Caycedo (1978).

Thirty sea cucumber specimens (different sizes and color) were collected from the field at the fishing areas. A slice 1 c[m.sup.2] x 1 mm thick was dissected from the dorsal epidermis of each individual. In the laboratory, each sample was placed in a small test tube with 3 mL of commercial bleach. Samples were left for approximately 60 min or until the body wall had dissolved and the ossicles settled to the bottom, resembling fine white sediment. Using a pipette, the precipitated spicules were transferred to a microscope slide, covered with a coverslip and the spicules morphology was examined with a microscope at 40x and 100x magnification (Hickman, 1998). For the determination of species, we used the identification keys of Caycedo (1978), Pawson & Pawson (2008) and De Entrambasaguas (2008).


To estimate sea cucumber density, data were collected by fisherman and by us. In each site (10) were set belt transects 50 m long and 4 m wide (Fig. 1) during the official fishing season (April-May 2011 and FebruaryMarch 2012). All organisms observed within transects were collected using hookah diving (10 to 25 m depth), placed in mesh bags, transported to the boat, and put in a cooler with ice and seawater, this method is used by all fishermen to preserve the product, thus producing a relaxation in the organisms. In September 2011, out of the fishing season, eight transects were installed in the same area, and sea cucumbers were counted, but not collected.

Sea cucumbers were measured for total length ([L.sub.t]) using a flexible plastic tape, 1 mm precision; along the dorsal profile of the body. The total and eviscerated weight of each sea cucumber was registered with an electronic balance at 0.5 g precision. The weight-length relationship [W.sub.t] = a [L.sub.t.sup.b] (Cone, 1989) was obtained by using data from May 2011 and February 2012.

Length-frequency data analysis

With the data of May 2011, February and March 2012 and the size-frequency data, grouped in 1 cm modal composition intervals, were calculated the parameters of the von Bertalanffy growth model (Ricker, 1975) using the computer software FiSAT II (Gayanilo et al., 1996). The following routines were used: PowellWetherall (to estimate [L.sub.[infinity]]), Shepherd (to estimate K, individual growth coefficient), and Pauly's (1984) empirical equation (to obtain t0, the theoretical age at zero length) and the length-weight relationship was calculated. Total mortality (Z) was calculated by the catch curve, natural mortality was obtained according to Pauly's equation; whereas exploitation rate was calculated with E = F/Z, and considering that [E.sub.optims] occurs when F = M (Gayanilo et al., 1996).


The shape and composition of the spicules embedded in the body wall are frequently used as taxonomic characters. In the case of I. badionotus in Sisal, the spicules remained intact, with little fractioning (especially of the plates), and the proportion of different types of spicules were constant in the different samples. According to the morphometric analysis of the calcareous ossicles, and based in the presence higher percentage of towers and plates with dishes with homogeneous size hole, and specific structures like C-Shaped spicules in less proportion and rods present exclusively in this species, as mentioned in the taxonomic key by Caycedo (1978), we found that 99% of the catch corresponded to I. badionotus (Fig. 2).

Mean density in April 2011 was 0.84 [+ or -] 0.40 ind [m.sup.-2], with a maximum at S4 of 1.43 ind [m.sup.-2]. Density showed a downward trend in the following sampling months: in September mean density was 0.51 [+ or -] 0.46 ind [m.sup.-2], whereas in February 2012 was 0.32 [+ or -] 0.17 ind [m.sup.-2], considering the global mean density for all months we obtained 0.5570 [+ or -] 0.345 ind [m.sup.-2] (Table 1).

A total of 7,618 sea cucumbers were measured in the harbor, during the fishing seasons, 2,615 corresponded to May 2011, 970 to February 2012 and 4,033 to March 2012. The data collected in April 2011 (2,732) were used only for density calculations and size analysis, however, they were not including in the population parameters analysis.

Sea cucumber's length varied from 90 to 420 mm. In April 2011 the mean size was 226.10 [+ or -] 4.31 mm, and in May 2011 the median size was 228.50 [+ or -] 4.07 mm (Figs. 3a-3b). During 2012, we registered a median size of 236.10 [+ or -] 2.79 mm in February, whereas in March was 249.40 [+ or -] 3.65 mm (Figs. 4a-4b). In all cases, the distribution of frequencies was unimodal.

With the length frequency data, we determined the von Bertalanffy equation to be Lt = 403 (1-[e.sup.-(025(t-018))]). The total mortality rate was 0.88, with a natural mortality of 0.38. In consequence, the fish mortality was 0.50 and the exploitation rate 0.54.

The values of the coefficients of the weight-length equation were: a = 2.811 and the exponent b = 1.741. The correlation coefficient was R2 = 0.72 (Fig. 5). A Student's t-test was applied confirming that the growth was allometric (P < 0.05).


In the Yucatan Peninsula, three commercial species of sea cucumbers have been reported: A. multifidus, I. badionotus, and H. floridana (Zetina-Moguel et al., 2003), the same species composition was reported by Rodriguez-Gil (2007) in the area of Progresso. Apparently, there is a specific distribution of sea cucumbers in the Yucatan Peninsula: H. floridana and A. multifidus are most abundant in the Campeche coast, whereas I. badionotus is more abundant in the Yucatan coast, with a minor abundance of H. floridana (Ramos, pers. comm.). In this study we found that 99% of the catch corresponded to I. badionotus, confirming that I. badionotus is the most abundant species in Yucatan coast.

The mean global density, considering both sampling periods, was 5570 ind [ha.sup.-1], a similar value to other countries. In Cuba, a density of 8,800 ind [h.sup.a-1] has been reported in an established fishery (Alfonso et al., 2000; Toral-Granda et al., 2008). In the Yucatan coast, Lopez-Rocha (2011) found a median density 217 ind [ha.sup.-1] for I. badionotus in Sisal, whereas Rodriguez-Gil (2007) found a density varying between, 267 to 437 ind [ha.sup.-1] in Progreso, Yucatan. Density evaluations carried out in 2000-2001 at the central and east coast of Yucatan were significantly lower and varied from 5 to 25 ind [ha.sup.-1] (Rodriguez-Gil, 2007). A density of 0.072 ind [m.sup.-2] was reported by Poot-Salazar et al. (2015) in fishing areas near to Progreso Yucatan and a similar value was informed by Hernandez-Flores et al. (2015). There are no more data for this fishing area; however, it is evident that the differences in density may be due to different sampling methods, or heterogeneous and patchy distribution of sea cucumber, which may lead to underestimating densities (Lopez-Rocha, 2011). In Panama, population surveys showed that H. mexicana was the most abundant species (161.8 ind [ha.sup.-1]), followed by I. badionotus (117.4 ind [ha.sup.-1]) (Guzman & Guevara, 2002). In Baja California, Mexico, ReyesBonilla et al. (2008) found a density of 1000 ind [ha.sup.-1] for I. fuscus in Cabo Loreto National Marine Park, whereas in Galapagos Island, a density 230 ind [ha.sup.-1] was shown by Toral-Granda & Martinez (2004), in both sites there is an intense fishing of sea cucumber.

The size structure was unimodal, with a median size of 220 mm and a range from 95 to 420 mm, with a high abundance of adults; this pattern is shared with other data collected in the Caribbean. In Panama, Guzman & Guevara (2002) also found a unimodal distribution, with a median size of 250 mm. The unimodal population structures of I. badionotus may indicate a constant recruitment to the populations (Avalos-Castillo et al., 2017). Lopez-Rocha (2011) found in Sisal, Yucatan, that length varied from 140 to 300 mm with a mean length of 220 mm, whereas Poot-Salazar et al. (2015) informed of a medium size of 230 mm to I. badionotus at Sisal and considering the resource overexploited. Reports from fisheries in Venezuela indicate sizes between 110-320 mm for I. badionotus (Buitrago & Boada, 1996; Rodriguez-Milliet & Pauls, 1998). The latter reports suggest that the fishery was based on individuals somewhat below the minimum reproductive age, estimated at 180 mm for I. badionotus (Buitrago & Boada, 1996; Rodriguez-Milliet & Pauls, 1998). Considering the size structure in Venezuela, similar lengths were obtained for I. badionotus (200-300 mm) (Rodriguez-Milliet & Pauls, 1998). There are no reports on growth parameters of I. badionotus in the Gulf of Mexico, but it is clear that the species has a low growth rate, with adult lengths varying from 350 to 500 mm. Herrero-Perezrul et al. (1999) found a growth equation for I. fuscus with similar growth parameters (b = 1.83; a = 1.142) as I. badionotus in the Gulf of Mexico.

Most sea cucumbers grow allometrically (Bulteel et al., 1999). Probably because small individuals are relatively flatter than adults, suggesting that the change in shape and inner volume may be necessary to allow gonad growth (Toral-Granda et al., 2008). In Yucatan, Lopez-Rocha (2011) also reported an allometric growth, with b = 1.045 and a = 27.44 ([R.sup.2] = 0.3685), whereas Herrero-Perezrul & Reyes-Bonilla (2008) as well found an allometric growth in the case of I. fuscus in Espiritu Santo, Baja California.

In general, it is accepted that the invertebrate fisheries are developed with species without previous biological or density information and this is true for sea cucumbers (Lovateli et al., 2004; Anderson et al., 2011). It is very important to generate fishery and biological information, in order to establish the first management measures for the resource exploitation. The high demand and economic value of some sea cucumber species have led to its exploitation in sites where they are not regionally consumed. The lack of information and management strategies may cause overexploitation. Sea cucumbers are susceptible to overexploitation due to many factors: low mobility, distribution in shallow waters, late maturity, densitydependent reproduction, and low recruitment (Conand 1983, 2005).

It has been accepted that sea cucumbers fisheries worldwide are generally poorly managed and many of them are in decline (Perry et al., 1999; Toral-Granda et al., 2008; Anderson et al., 2011). Little is known for all sea cucumber species in the Gulf of Mexico, with sparse information on the few species that may be of commercial interest. The ecology and larval distribution of I. badionotus are unknown, as with many species of sea cucumber (Conand, 1983). Density and size distribution are parameters that define the state of the fishery in any moment, a density higher than 0.45 ind [ha.sup.-1] may permit the ecological and biological cycles in sea cucumber populations (Toral-Granda & Martinez, 2004). At Sisal there seems to exist a high sea cucumber density, and the population is composed of adults. However, it is necessary to design management strategies to protect the resource of overexploitation such as: establish an annual catch quota, catching size (>280 mm total length), implement a surveying program of the population density, and initiate studies on reproduction and larvae distribution research.

DOI: 10.3856/vol46-issue2-fulltext-17


We appreciate very much the comments of Frank Ocana, Jacobo Schmitter Soto, Ashleigh Smythe, David Gonzalez and two anonymous reviewers. Holger Wiessemberger drew the Figure 1. The collaboration of the Sisal Cooperative fishermen, especially to Jose May was very important.


Alfonso, I., M.P Frias, M. Vilaragut, I. Tellez, J.M. Morales & C.A. Reyes. 2000. Estado actual del recurso pepino de mar en la plataforma sur oriental de Cuba. 2000. Third Congress on Marine Sciences 'Marcuba 2000', Havana City, 13 pp.

Anderson, S.C., J.M. Flemming, R. Watson & H.L. Lotze. 2011. Serial exploitation of global sea cucumber fisheries. Fish Fish., 12: 317-339.

Avalos-Castillo, C.G., J.R. Ortiz, A.J. Pacay Barahona & F.M. Polanco Vasquez. 2017. Evaluacion del estado poblacional del pepino de mar (Clase Holoturoidea) en el Caribe de Guatemala. Informe Final, Universidad de San Carlos de Guatemala Direccion General de Investigacion Programa Universitario de Investigacion en Recursos Naturales y Ambiente, 55 pp.

Bruckner, A.W. 2006. Proceedings of the technical workshop on the conservation of sea cucumbers in the families Holothuridae and Stichopodidae. NOAA Tech. Mem. NMFS-OPR 34, Silver Spring, MD, 244 pp.

Bruckner, A.W., K.A. Johnson & J.D. Field. 2003. Conservation strategies for sea cucumbers: can a CITES Appendix II listing promote sustainable international trade? SPC Beche-de-Mer Inf. Bull., 18: 24-33.

Buitrago, J. & J.A. Boada. 1996. La pesca de la holoturia Isostichopus badionotus en el oriente de Venezuela. Mem. Soc. Cienc. Nat. La Salle, 146: 33-40.

Bulteel, P., M. Jangoux & P. Coulon. 1999. Biometry, bathymetric distribution, and reproductive cycle of the holothuroid Holothuria tubulosa (Echinodermata) from the Mediterranean seagrass beds. P.S.Z.N.I. Mar. Ecol., 13(1): 53-62.

Caycedo, I.E. 1978. Holothuroidea (Echinodermata) de aguas someras en la costa norte de Colombia. Ann. Inst. Invest. Mar. Punta Betin, 10: 149-198.

Conand C. 1983. Methodes d'etude de la croissance des holothuries et premiers resultats d'une experience de marquage en Nouvelle-Caledonie. Lettre d'Information sur les Peches de la CPS, 26: 33-40.

Conand, C. 1997. Are holothurian fisheries for export sustainable? Proceedings 8th International Coral Reefs Symposium, Panama, 2: 2021-2026.

Conand, C. 2005. Sea cucumber biology, taxonomy, distribution, biology, conservation status. In: A. Bruckner (ed.). Proceedings of the technical workshop on the conservation of sea cucumbers in the Families Holothuridae and Stichopodidae. NOAA Tech. Mem. NMFS-OPR 44, Silver Spring, MD, 33-50. pp.

Conand, C. 2017. Expansion of global sea cucumber fisheries buoys exports. Rev. Biol. Trop. 65(Suppl. 1): 1-10.

Cone, R.S. 1989. The need to reconsider the use of condition index in fishery science. T. Am. Fish. Soc., 118: 510-514.

De Entrambasaguas, M.L. 2008. Estudio faunistico y ecologico de los equinodermos del archipielago de Cabo Verde. Departamento de Ecologia e Hidrologia Facultad de Biologia, Universidad de Murcia, pp. 134-138.

De la Fuente-Betancourt, G.L., A. de Jesus-Navarrete, E. Sosa-Cordero & M.D. Herrero-Perezrul. 2001. Assessment of the sea cucumber (Echinodermata: Holothuroidea) as potencial fishery resource in Banco Chinchorro, Quintana Roo, Mexico. Bull. Mar Sci., 68: 59-67.

Delgado-Carranza, C., F. Bautista, R. Orellana-Lanza & H. Reyes-Hernandez. 2011. Classification and agroclimatic zoning using the relationship between precipitation and evapotranspiration in the State of Yucatan, Mexico. Invest. Geogr. Bol. Inst. Geogr., UNAM, 75: 51-60.

Diario de Yucatan. 2011. Captura ilegal de pepino de mar en Sisal y Progreso Yucatan. Diario de Yucatan, Seccion Progreso, 8 pp.

Diario Oficial de la Federacion (DOF). 2011. Acuerdo por el que se modifica el aviso por el que se da a conocer el establecimiento de epocas y zonas de veda para la pesca de diferentes especies de la fauna acuatica en aguas de jurisdiccion federal de los Estados Unidos Mexicanos, publicado el 16 de marzo de 1994. Diario Oficial de la Federacion (Federal Gazette) 19 Diciembre 2011, Mexico.

Fajardo-Leon, M.C. & A. Velez-Barajas. 1996. Pesqueria del pepino de mar. In: M.C. Casas-Valdez & G. PonceDiaz (eds.). Estudio del potencial pesquero y acuicola de Baja California Sur. SEMARNAP/CICIMAR, pp. 151-165.

Gayanilo, F., P. Sparre & D. Pauly. 1996 The FAOICLARM stock assessment tools (FISAT) user's guide. FAO Comp. Inf. Ser. Fish., 7 pp.

Guzman, H.M. & C.A. Guevara. 2002. Population structure, distribution, and abundance of three commercial species of sea cucumber (Echinodermata) in Panama. Caribb. J. Sci., 38(3-4): 230-238.

Hernandez-Flores, A.D., A. Condal, A. Poot-Salazar & J.C. Espinoza-Mendez. 2015. Geostatistical analysis and spatial modeling of population density for the sea cucumbers Isostichopus badionotus and Holothuria floridana on the Yucatan Peninsula, Mexico. Fish. Res., 172: 114-124.

Herrero-Perezrul, M.D. & H. Reyes-Bonilla. 2008. Weight-length relationship and relative condition of the holothurian Isostichopus fuscus at Espiritu Santo Island, Gulf of California, Mexico. Rev. Biol. Trop., 56(Suppl. 3): 273-280.

Herrero-Perezrul, M.D., H. Reyes-Bonilla, F. Garcia-Dominguez & C.E. Cintra-Buenrostro. 1999. Reproduction and growth of Isostichopus fuscus (Ludwig, 1875) (Echinodermata: Holothuroidea) in the southern Gulf of California, Mexico. Mar. Biol., 135: 521-532.

Hickman, C.J. 1998. A field guide to sea stars and other echinoderms of Galapagos. Sugar Spring Press, Lexington, 83 pp.

Lopez-Rocha, J.A. 2011. Distribucion y abundancia del pepino de mar Isostichopus badionotus frente a la costa de Sisal, Yucatan. Proc. Gulf Caribb. Fish. Inst., 64: 153-160.

Lovatelli, A., C. Conand, S. Purcell, S. Uthicke, S. Hamel & J.F. Mercier. 2004. Advances in sea cucumber aquaculture and management. FAO Fish. Tech. Pap., 463: 425 pp.

Pauly, D. 1984. Fish population dynamics in tropical water: a manual for use with a programmable calculator. ICLARM Stud. Rev., 8: 325 pp.

Pawson, D.L. & D. Pawson. 2008. An illustrated key to the sea cucumbers of the South Atlantic Bight. Smithsonian Institution, Washington, DC., pp. 20013-27012.

Perry, R.I., C.J. Walters & J.A. Boutillier. 1999. A framework for providing scientific advice for the management of new and developing invertebrate fisheries. Rev. Fish Biol. Fish., 9: 125-150.

Poot-Salazar, A., A. Hernandez-Flores & P.L. Ardisson. 2015. Indicadores de sostenibilidad para la evaluacion de las pesquerias de pepino de mar en la peninsula de Yucatan, Mexico. Cienc. Pesq., 23(2): 11-24.

Reyes-Bonilla, H. & M.D. Herrero-Perezrul. 2003. Population parameters of an exploited population of Isostichopus fuscus (Holothuroidea) in the Southern Gulf of California, Mexico. Fish Rev., 59: 423-430.

Reyes-Bonilla, H., M.D. Herrero-Perezrul, S. GonzalezRomero, A. Gonzalez-Peralta & Y. RamirezHernandez. 2008. Abundance of the brown sea cucumber Isostichopus fuscus at the National Park Bahia de Loreto, Mexico. Rev. Biol. Trop., 56(Suppl. 3): 265-271.

Ricker, W.C. 1975. Computation and interpretation of biological statistics of fish populations. Bull. Fish. Res. Bd. Can., 191: 1-382.

Rodriguez-Gil, L.A. 2007. El pepino de mar como un recurso potencial de la costa del Estado de Yucatan, Mexico. Proc. Gulf Caribb. Fish. Inst., 59: 255-262.

Rodriguez-Milliet, E. & S.M. Pauls. 1998. Sea cucumbers fisheries in Venezuela. Proceedings of 9th International Echinoderm Conference, pp. 513-516.

Toral-Granda, M.V., A. Lovatelli & M. Vasconcelos. 2008. Sea cucumbers. A global review of fisheries and trade. 2008. FAO Fish. Aquacult. Tech. Pap., 516: 317 pp.

Toral-Granda, M.V. & P.C. Martinez. 2004. Population density and fishery impacts on the sea cucumber (Isostichopus fuscus) in the Galapagos Marine Reserve. In: C. Lovatelli, S. Conand, S. Purcell, J. Uthicke, F. Hamel & A. Mercier (eds.). Advances in sea cucumber aquaculture and management. FAO Fish. Tech. Paper, 463: 91-100.

Zetina-Moguel, C., V. Rios-Lara, M. Koyoc-Cruz, I. Hernandez, K. Cervera-Cervera, D. De Anda-Fuentes, P. Arceo-Briseno, E. Ortiz & M. Guevara-Ortiz. 2003. Estimacion de la biomasa de pepino de mar (Astichopus multifidus, Isostichopus badionotus y Holoturia floridana) en dos areas de la costa de Yucatan entre octubre del 2000 y marzo del 2001. Proc. Gulf Caribb. Fish. Inst., 54: 297-306.

Received: 18 October 2016; Accepted: 11 January 2018

Alberto de Jesus-Navarrete (1), Maria Nallely May Poot (2) & Alejandro Medina- Quej (2)

(1) Departamento de Sistematica y Ecologia Acuatica, Estructura y Funcion del Bentos El Colegio de la Frontera Sur, Quintana Roo, Mexico

(2) Instituto Tecnologico de Chetumal, Licenciatura en Biologia, Chetumal, Quintana Roo, Mexico

Corresponding author: Alberto de Jesus-Navarrete (

Corresponding editor: Diego Giberto

Captions: Figure 1. Study area and sampling points at Sisal, Yucatan.

Captions: Figure. 2. a) General image of calcareous spicules specific to I. badionotus (Bar = 30 [micro]m), b) towers, c) C-shaped spicules, and d) disk (Bar = 30 [micro]m).

Captions: Figure 3. Length-frequency distribution of sea cucumbers at Sisal Yucatan, samples collected in a) April, and b) May 2011.

Captions: Figure 4. Length-frequency distribution of sea cucumbers at Sisal Yucatan, samples collected in a) February 2012, and b) March 2012.

Captions: Figure 5. Weight-length relationship of the sea cucumber I. badionotus at Sisal, Yucatan, Mexico.
Table 1. Sea cucumber (I. badionotus) density in
transects at fishing areas at Sisal Yucatan, Mexico.

                     Sampled area ([m.sup.2])      No individuals

Transect             Apr        Sep        Feb    Apr      Sep     Feb
1                    200        200        200     24      294     45
2                    200        200        200    173      188     62
3                    200        200        200    220      55      13
4                    200        200        200    286      99      135
5                    200        200        200     72      36      51
6                    200        200        200    187      56      53
7                    200        200        200    230      29      64
8                    200        200        200    148      65      24
9                    200                   200    176              81
10                                         200                     42
Total sea
  cucumbers         1800       1600       2200   1516     822     706
Mean density
Standard deviation

                      Density (ind [m.sup.-2]   [Global
Transect              Apr      Sep      Feb      mean

1                     0.12     1.47     0.23
2                     0.86     0.94     0.31
3                     1.1      0.28     0.07
4                     1.43     0.5      0.67
5                     0.36     0.18     0.26
6                     0.93     0.28     0.27
7                     1.15     0.15     0.32
8                     0.74     0.33     0.12
9                     0.88              0.41
10                                      0.21
Total sea cucumbers
Mean density          0.84     0.51     0.32     0.557
Standard deviation    0.40     0.46     0.17     0.345
COPYRIGHT 2018 Pontificia Universidad Catolica de Valparaiso, Escuela de Ciencias del Mar
No portion of this article can be reproduced without the express written permission from the copyright holder.
Copyright 2018 Gale, Cengage Learning. All rights reserved.

Article Details
Printer friendly Cite/link Email Feedback
Title Annotation:Research Article
Author:de Jesus-Navarrete, Alberto; Poot, Maria Nallely May; Medina-Quej, Alejandro
Publication:Latin American Journal of Aquatic Research
Date:May 1, 2018
Previous Article:Population dynamics and secondary production of Darina solenoides (Bivalvia: Mactridae) in the Rio Gallegos Estuary, southern Patagonia.
Next Article:Proposal of an integrated system for forecasting Harmful Algal Blooms (HAB) in Chile.

Terms of use | Privacy policy | Copyright © 2021 Farlex, Inc. | Feedback | For webmasters |