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Distribucion espacial de Eufausidos (Euphausiacea) en la Isla Malpelo, Pacifico Tropical de Colombia.

Spatial distribution of Euphausiids (Euphausiacea) off Malpelo Island, Colombian Tropical Pacific

Malpelo Island is the only Colombian oceanic insular territory in the Pacific Ocean. It consists of the emergent part of a submarine mountain range called the Malpelo Dorsal. The island and the surrounding 26 679 [km.sup.2] area encompass a marine protected area in the category of Fauna and Flora Sanctuary (MMA, 1995; MADS, 2017) established in 1995. One of the main challenges in administrating and protecting a marine area is obtaining knowledge on the different taxonomic groups that inhabit it (Pomeroy, Parks, & Watson, 2004). Therefore, efforts to establish trustworthy taxonomic information that would allow not only the quantification of biological diversity at a location, but also the identification of research themes required to strengthen management actions, are highly relevant.

Euphausiids comprise one of the zooplankton taxonomic groups with the least research effort thus far for the Colombian Pacific. Euphausiids are holoplanktonic crustaceans who carry out vertical migrations in the water column as part of their diel cycle. These migrations make them a key element in the biological pump of the pelagic environment worldwide (Werner & Buchholz, 2013; Sogawa et al., 2016; Wiebe, Bucklin, Kaartvedt, R0stad, & Blanco-Bercial, 2016). They also play an important role in marine trophic webs, as they represent a food source for several squid, fish, bird, and mammal species (Pauly, Trites, Capuli, & Christensen, 1998; Estrada, Lutcavage, & Thorrold, 2005; Zeidberg & Robison, 2007; Hipfner, 2009).

Although research on this taxonomic group has been wide-ranging in the Eastern Pacific (see review in Fernandez-Alamo & Farber-Lorda, 2006), research has mostly been concentrated in some regions such as the California Current (e.g. Brinton & Townsend, 2003; Ressler et al., 2005; Santora, Sydeman, Schroeder, Wells, & Field, 2011), the Humboldt Current (e.g. Linacre & Palma, 2004; Gonzalez et al., 2009; Antezana, 2010), and the Mexican Tropical Pacific (e.g. Farber-Lorda, Trasvina, & Cortes-Verdin, 2010; AmbrizArreola, Gomez-Gutierrez, Franco-Gordo, Lavaniegos, & Godinez-Dominguez, 2012). There have been few recent studies, except for the Mexican Tropical Pacific, where different aspects related to biological and ecological processes of this taxonomic group have been evaluated (Lopez-Cortes, 1990; Farber-Lorda, Lavin, Zapatero, & Robles, 1994; Gomez-Gutierrez et al., 2014). Studies on euphausiids in the remaining geographic area of the Eastern Tropical Pacific (ETP) were carried out in the 1960's, and were focused on taxonomic identity and general spatial distribution patterns (Brinton, 1962; 1979), being scarce the studies realized in recent times.

For the ETP, which includes the Colombian Pacific, scientific studies on euphausiids have been carried out by Sameoto, Guglielmo & Lewis (1987), who evaluated the temporal variation in vertical migration of euphausiids associated with the Costa Rica Dome, and by Azofeifa-Solano, Corrales-Ugalde, Castellanos-Osorio, & Morales-Ramirez (2016), who carried out a taxonomic analysis of euphausiids associated with Cocos Island. Two studies have been published for the Colombian Pacific, one by Carvajal, Vergara & Lopez (2009) who analyzed the effects of El Nino and La Nina on four taxonomic groups at the genus level, including euphausiids, and one by Lopez & Medellin (2010), who described the taxonomic composition and spatial variation in abundance of euphausiids in superficial samples taken in the Colombian Pacific Basin in July 2006.

Considering the importance of euphausiids as an integral part and key component of oceanic food webs, the scarce information available on this taxonomic group in the Colombian Pacific, and the need to generate relevant technical information to strengthen management processes in the only protected oceanic area in the Colombian Pacific, the present study was carried out to identify taxonomically the euphausiids associated with the Malpelo Island protected area. Furthermore, the spatial variation in abundance in September 2012 is described, and the vertical migration pattern of dominant species is analyzed.


Zooplankton samples used in this study were obtained during the ERFEN XV-CPC LI oceanographic campaign carried out in September 2012 aboard the ARC Providencia research vessel, ascribed to the Navy National Armed Forces and administered by the Maritime General Direction-DIMAR of Colombia. The oceanographic conditions at this location are strongly influenced by the Panama wind jet and by the intertropical convergence zone (Villegas & Malikov, 2006; Villegas, Malikov & Diaz, 2016). The 21 [degrees]C isotherm occurs between 30 and 35 m depth year-round, and the 15 [degrees]C isotherm occurs at 70 m depth during the first months of the year, and at over 125 m depth during the second semester of the year (Rodriguez-Rubio & Giraldo, 2011). The sampling grid comprised 10 biological stations distributed around Malpelo Island (Fig. 1). Temperature and salinity were recorded at each station, at standard depths ranging from 0 to 200 m. Vertical zooplankton samples were obtained using an oceanographic vertical net 0.3 m in diameter, 1.8 m in length, and of 250 [micro]m mesh size, including a General Oceanics Open-Close system at three depth layers: 0-50, 50-100, and 100-150 m. Zooplankton sampling was carried out only at the first two layers if depth at the station did not allow for deeper sampling. Samples were preserved in buffered formaldehyde at a final 4% concentration and transported to the laboratory of the Oceanographic Sciences Research Group of the Universidad del Valle.

Euphausiids present in the total sample were identified in the laboratory to the lowest taxonomic level possible using the guides by Boden, Johnson & Brinton (1955), Baker, Boden, & Brinton (1990), Gibbons Spiridonov, & Tarling (1999) y Brinton, Ohman, Townsend, Knight, & Bridgeman (2000). The recommendation of Brinton et al. (2000) regarding calyptopis and furcilia larvae of the group 1-A was followed; they were distributed proportionally according to the abundance of juveniles and adults of the species belonging to that classification (in this study, Euphausia eximia and Euphausia diomedeae, for which the proportions were 30 and 70 %, respectively). Counts were standardized (individuals/1 000[m.sup.3]) based on the volume of filtered water estimated based on the distance travelled by the net (50 m) and the mouth area.

The richness estimators ICE, Chao-2, Bootstrapping and first order Jacknife, established by resampling (n = 1 000) (EstimateS v 8.0), were used to evaluate the effectiveness of sampling effort. The influence of layer depth and sampling time (day/night) on euphausiid abundance was estimated. As data did not meet the assumptions of normality and homogeneity of variances, generalized linear models with quasi-Poisson distribution, which had the best data adjustment, were used. These analyses were performed using the program R.

Taking into account the total abundance at the 0-50 m vs. 50-100 m, and 50-100 m vs. 100-150 m layers, the Vertical Distribution Index (VDI) was calculated as VDI = ln (n1 /n2), where n1 is the abundance of species i in the upper layer, and n2 is the abundance of species i in the layer below. Finally, the spatial distribution in the abundance of each identified species was described, taking into account the three depth layers, using Surfer[R] v9 software.


The superficial temperature during the sampling period was 26.90 [+ or -] 0.18 [degrees]C in the study area. The 21 [degrees]C isotherm was located at 50 m depth (Fig. 2). Superficial salinity was variable, with records ranging between 30.52 and 32.54. However, the salinity record stabilized at 32.50 between 10 and 30 m depth, and the halocline was located at 50 m (Fig. 2).

A total of 10 species belonging to four genera (Euphausia, Stylocheiron, Nematoscelis, and Nematobrachion) were identified (Table 1). The four estimators used to evaluate the effectiveness of sampling confirmed that the effort represented adequately the composition of the euphausiid assemblage in the study area (Fig. 3).

The 50-100 m layer had the highest average abundance, considering only the stations at which it was possible to evaluate all three layers (Fig. 4). The euphausiid abundance in the 50-100 m layer was significantly higher than in the 100-150 m layer (p<0.05), and, the abundance in the 50-100 m layer was higher than the 0-50 m layer, although differences were not significant (p=0.06). Besides, there were no significant differences in abundance between the 0-50 m and 100-150 m layers (p=0.12). Sampling time did not affect significantly euphausiid abundance at the three depth layers (p=0.94).

Although defined vertical migration pattern with respect to time of day was not identified, the VDI suggested that euphausiid species were concentrated in the 50-100 m layer during night and day. Moreover, the VDI indicated that euphausiids were found in the 50-100 and 100-150 m layers independently of the time of day (Fig. 5).

None of the species was present at all sampling stations. However, the three most abundant species were widely distributed around the island at the three depth layers. Stylocheiron carinatum was the fifth most abundant species; it was present only at the western sector of the island in the 50-100 m layer and was not abundant in the 0-50 and 100-150 m layers (Fig. 6).

The dominant developmental phases at the three depth layers were calyptopis larvae, following by furcilia larvae, juveniles, and adults. Adults increased in abundance gradually from the upper layer down to the deepest layer, whereas juveniles presented the opposite pattern. Calyptopis as well as furcilia larvae were found in similar proportions at the three layers (Table 2).


The ten species identified in this study have tropical and subtropical affinity (Brinton, 1962; Brinton et al., 2000) and are considered new records for Malpelo Island; however, all species have already been recorded for the Colombian Pacific (Rivera & Giraldo, in press). Recently, Azofeifa-Solano et al. (2016) reported the presence of 13 euphausiid species around Cocos Island, Costa Rica, an oceanic insular environment similar to Malpelo Island, with 100 % of species recorded in Malpelo Island also recorded at Cocos Island. However, the specific richness of euphausiids at Malpelo Island was lower than that reported for other oceanic subtropical Eastern Pacific insular environments, such as the Juan Fernandez Archipelago and the Desventuradas Islands in Chile, where 22 euphausiid species have been reported (Mujica & Pavez, 2008). There is probably a confluence of species with tropical and subpolar affinity in subtropical regions, which would result in an increase in local specific richness, whereas in a tropical environment such as Malpelo Island we would only expect species with tropical affinity.

The abundant record of larval phases (calyptopis and furcilia) confirms the occurrence of active reproductive processes in this region. The type of net used during this study could have biased captures against adult specimens, because these organisms have greater swimming ability and their eyes are completely developed, which allows them to avoid nets (Mathew, 1988; Brierley, 1999; Everson, 2000). In the study carried out by Sameoto et al. (1987) in the Costa Rica Dome, the highest capture proportion was of adult individuals. In that study zooplankton captures were obtained with oblique tows, using a 1 [m.sup.2] net at a speed of 2 knots, whereas during the present study zooplankton captures were obtained with vertical tows, using a 0.3 [m.sup.2] area net at a speed of 0.5 knots. Despite this limitation, the sampling effort represented adequately the taxonomic composition of the euphausiid assemblage in the study area.

Most euphausiid species in Malpelo Island were located at the 50-100 m layer. A study by Andersen, Sardou & Gasser (1997) reported that the highest euphausiid concentration occurred at between 0 and 150 m in eutrophic and mesotrophic sites, whereas in oligotrophic environments the trend was towards an almost uniform distribution between 0 and 700 m depth in the tropical Northeast Atlantic. In general, the depth range at which the highest abundance of euphausiids concentrates is valid for adults as well as for larvae; however, it should be noted that vertical migration also depends on the developmental phase (Escribano, Marin, & Irribarren, 2000), so that juveniles and adults migrate more than larvae, which are probably always in the superficial layer.

The fact that there were no significant differences in euphausiid abundance between diurnal and nocturnal stations suggests that net evasion could have been equally effective during day and night, or that there was no significant evasion despite the evidence of net evasion by euphausiids in previous studies, established mainly based on differences in abundance between diurnal and nocturnal stations, with nocturnal stations presenting greater abundance (Brinton, 1967; Mathew, 1988). Sameoto et al. (1987) reported greater biomass and total abundance of euphausiids in the day compared with night in the Costa Rica Dome, and presence of rare species captured only at night, similarly to what occurred in this study for Malpelo Island, considering the case of Nematobrachion flexipes, which was only present at a nocturnal station in the 100-150 m layer.

There were adults of five species (E. diomedeae, E. distinguenda, E. tenera, N. gracilis, and S. carinatum) at the three depth layers only at the nocturnal stations, which coincides with the vertical distribution ranges of these species during nighttime hours, as it has been reported that E. diomedeae adults can be found at the surface and at 75 m depth during the night, whereas they are found at between 250 and 350 m during the day. E. distinguenda is found at between 300 and 400 m during the day, and above 50 m at night; E. tenera is found at between the surface and 140 m at night, and between 150 and 300 m during the day; N. gracilis has been reported to be between 100 and 300 m at night, and at between 300 and 500 m during the day; and S. carinatum remains between the surface and 140 m during the night (Brinton, 1962; Brinton et al., 2000).

Euphausia distinguenda was the most abundant species around Malpelo Island and the most abundant in the 50-100 m layer. The larval and juvenile phases of this species predominated and were present at the three depth layers during the day and night, despite Brinton et al. (2000) giving a range for adults of this species of 300 to 400 m during the day and above 50 m at night. Sameoto et al. (1987) found that E. distinguenda was the dominant species at two stations in the Costa Rica Dome, with greatest concentrations at between 250 and 450 m during the day and night, but with an abundance peak at night above the thermocline (10-50 m).

Roger (1971) reported Euphausia diomedeae as the most abundant species in the 0-100 m layer, representing 94 % of the total species in that layer; he did not report it below 100 m, which suggests that E. diomedeae did not cross the thermocline, which was at between 100 and 160 m depth in that study. In the present study, E. diomedeae was the most abundant species in the 0-50 m and 100-150 m layers around Malpelo Island, which suggests that contrary to Roger's study (1971) it crossed the thermocline, which has been reported at 70 m depth at the beginning of the year, and at 125 m during the second part of the year around Malpelo Island (Rodriguez-Rubio & Giraldo, 2011).

The abundance of Euphausia eximia was intermediate, but this species was widely distributed around Malpelo Island at the three depth layers. Its abundance did not vary significantly between the three layers, but it was greatest at between 50 and 100 m; this coincides with the study by Brinton et al. (2000), who reported E. eximia as a species migrating between the surface and 300 m depth. There were no adult organisms of this species, and juveniles were present only at nocturnal stations, similarly to what was reported by Andersen et al. (1997), with E. eximia present only at nocturnal stations in the tropical Atlantic.

Several authors have reported that Stylocheiron carinatum carries out short diel migrations (Brinton, 1967; Sameoto et al., 1987). For example, Brinton (1967) suggested that this species could carry out short migrations between the surface and 150 m during the day, and between the surface and 100 m at night. In the present study S. carinatum was captured mainly in the 50 to 100 m layer at diurnal as well as nocturnal stations, although it occurred at 0-50 m at one nocturnal station and at 100150 m at another nocturnal station, which suggests that this species could be found between the surface and 150 m during the day and night at Malpelo Island. This result is similar to that reported by Roger (1971) for the equatorial Pacific current system.

Stylocheiron affine was collected only in the 50 to 100 m layer. Despite the fact that it was not found at the deepest layer, the fact that it was not found between the surface and 50 m suggests that this species does not occur in the upper layer. Brinton et al. (2000) reported it as a species found above the thermocline, and suggested that it is present between the surface and the thermocline. However, results from the present study coincide with Roger (1971), who reported it at between 50 and 200 m, Hirota (1987) who recorded this species at around 100 m in the day and at between 50 and 300 m at night, and Youngbluth (1975), who reported it at between 50 and 250 m depth.

In conclusion, the present research study represents the first euphausiid record for Malpelo Island, Colombia. We described the spatial variation in abundance of this important taxonomic group in an insular location of the Eastern Tropical Pacific and established vertical variation patterns of the different species recorded at this location. It is necessary to direct research efforts towards quantifying the role of these organisms in energy transfer processes of the pelagic web of the oceanic environment of the Colombian Pacific, as well as evaluating their response to mesoscale oceanographic forcing such as El Nino/La Nina.

Ethical statement: authors declare that they all agree with this publication and made significant contributions; that there is no conflict of interest of any kind; and that we followed all pertinent ethical and legal procedures and requirements. A signed document has been filed in the journal archives.

Received 20-XII-2017. Corrected 31-VIII-2018. Accepted 07-XII-2018.


We thank Vanessa Izquierdo for her valuable help during zooplankton sampling. We thank the B.O. ARC Providencia crew for their unconditional support during the field phase of this investigation. We thank the General Maritime Direction (DIMAR) and the Center for Oceanographic and Hydrographic Research of the Pacific (CCCP) of the National Navy for their invitation to participate in sampling and analysis of the zooplankton component during the Oceanographic Campaign Pacifico LI-ERFEN XV and for carrying out the discrete record of temperature and salinity. This study was co-financed by DIMAR, CCCP, the Universidad del Valle, and the Programa Jovenes Investigadores e Innovadores Virginia Gutierrez de Pineda Convocatoria 617-2013, which benefitted the first author of this paper.


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Marisol Rivera Gomez & Alan Giraldo

Grupo de Investigacion en Ciencias Oceanograficas. Facultad de Ciencias Naturales y Exactas, Universidad del Valle, Ciudad Universitaria Melendez. Calle 13 No. 100-00 Cali, Colombia;,,

Caption: Fig. 1. Geographic location of the sample stations around Malpelo Island, Colombian Pacific, during the Oceanographic Campaign ERFEN XV-CPC LI in September 2012.

Caption: Fig. 2. Vertical variation of temperature ([degrees]C) and salinity in the study area during September 2012.

Caption: Fig. 3. Species accumulation curve of euphausiids, considering all depth stratums surveyed around Malpelo Island, during September 2012.

Caption: Fig. 4. Vertical distribution of the total abundance of euphausiids (ind. 1 000 [m.sup.-3]) in the three depth stratums surveyed around Malpelo Island, during September 2012.

Caption: Fig. 5. Vertical Distribution Index (VDI) as a function of the sampling time of total euphausiid abundance around Malpelo Island. Shaded area indicates nocturnal hours.

Caption: Fig. 6. Spatial distribution of the four more representative euphausiid species, for the three evaluated stratums, around Malpelo Island.
Species of euphausiids identified during September 2012 around
Malpelo Island

Species                                   Average abundance (ind. 1 000

                                          0-50 m   50-100 m   100-150 m

Euphausia distinguenda Hansen, 1911        396       594         340
Euphausia diomedeae Ortmann, 1894          430       357         413
Euphausia eximia Hansen, 1911              136       209         153
Euphausia tenera Hansen, 1905              141       170          0
Stylocheiron carinatum G.O. Sars, 1883      28       226         57
Nematoscelis gracilis Hansen, 1910         113       141          0
Euphausia lamelligera Hansen, 1911          85        0          113
Euphausia gibboides Ortmann, 1893           28        28         57
Stylocheiron affine Hansen, 1910            0         57          0
Nematobrachion flexipes Ortmann, 1893       0         0          57

Percentage of contribution to the total
of developmental phases by stratum

  Phase      0-50 m   50-100 m   100-150 m

Calyptopis   41.67     44.44       38.10
Furcilia     29.17     28.57       28.57
Juvenil      27.08     22.22       19.05
Adultos       2.08      4.76       14.29
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Author:Rivera Gomez, Marisol; Giraldo, Alan
Publication:Revista de Biologia Tropical
Date:Mar 1, 2019
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