MARINE AND FISHERY SCIENCES 36 (3): 245-265 (2023)
https://doi.org/10.47193/mafis.3632023010907
ABSTRACT. The Patagonian toothfish (Dissostichus eleginoides) is a commercially valuable
demersal fish present in the southern hemisphere. Therefore, understanding movements of the
species across time and spatial scales would enhance our understanding of its behavior within the
Argentine and Chilean Patagonian platform. The Instituto Nacional de Investigación y Desarrollo
Pesquero (INIDEP, Argentina) initiated a tag-recapture program for D. eleginoides in 2004. A total
of 5,907 specimens, mostly juveniles (<82 cm total length), have been tagged and released in waters
off the edge of the Argentine shelf and slope between 37° S and 47° S (northern Sector of the Argen-
tine fishing ground), and east of De los Estados Island and south of Tierra del Fuego (54° S-57° S
southern Sector of the Argentine fishing ground). A total of 121 specimens were recaptured: 25
(20.7%) were recovered in the northern Sector, 84 (69.4%) in the southern Sector and 12 (9.9%) in
waters of the Pacific Ocean in Chile. A total of 67.5% were recaptured within 20 nm (37 km) of the
release site and 15% traveled distances of less than 120 nm. A smaller fraction (5%) traveled dis-
tances between 120 and 400 nm and only 12.5% were recaptured at more than 400 nm. Using a Gen-
eralized Additive Model, it was determined that variables Days at liberty, Sector and Time of tag-
ging were influential in the distance traveled by specimens. From the present work, it seems evident
that this species possesses high site fidelity and lacks cyclic migratory movements involving a sub-
stantial component of the stock in the American southern cone.
Key words: Tagging, recapture, fishing ground, stock.
Patrones migratorios de la merluza negra (Dissostichus eleginoides) en el Océano Atlántico
Sudoccidental
RESUMEN. La merluza negra (Dissostichus eleginoides) es un pez demersal presente en el
hemisferio sur, muy valioso comercialmente. Por ello, comprender los movimientos en diferentes
escalas temporales y espaciales contribuiría a conocer más acerca del comportamiento que presenta
la especie en la plataforma patagónica argentina y chilena. Desde 2004, el Instituto Nacional de
Investigación y Desarrollo Pesquero (INIDEP, Argentina), inició un programa de marcado y recap-
tura de D. eleginoides. Un total de 5.907 ejemplares, en su mayoría juveniles (<82 cm de largo
total), fueron marcados y liberados en sectores ubicados en aguas del borde de la plataforma y talud
de la Argentina entre 37° S y 47° S (Sector norte del caladero argentino), y al este de la Isla de los
Estados y sur de Tierra del Fuego (54° S-57° S Sector sur del caladero argentino). Actualmente,
fueron recapturados 121 ejemplares, 25 (20,7%) se recuperaron en el Sector norte, 84 (69,4%) en
el Sector sur y 12 (9,9%) en aguas del Océano Pacífico en Chile. El 67,5% fue recapturado a menos
de 20 mn (37 km) del lugar de liberación y 15% recorrió distancias inferiores a las 120 mn. Una
fracción menor (5%) recorrió distancias entre 120 y 400 mn y solo 12,5% se recapturó a más de
400 mn. Mediante un Modelo Aditivo Generalizado se determinó que las variables Días en libertad,
Sector y Época de marcado influyeron en la distancia recorrida de los ejemplares. A partir del
245
*Correspondence:
gtroccoli@inidep.edu.ar
Received: 21 December 2022
Accepted: 2 June 2023
ISSN 2683-7595 (print)
ISSN 2683-7951 (online)
https://ojs.inidep.edu.ar
Journal of the Instituto Nacional de
Investigación y Desarrollo Pesquero
(INIDEP)
This work is licensed under a Creative
Commons Attribution-
NonCommercial-ShareAlike 4.0
International License
Marine and
Fishery Sciences
MAFIS
ORIGINAL RESEARCH
Migratory patterns of Patagonian toothfish (Dissostichus eleginoides) in the
southwestern Atlantic Ocean
GONZALO H. TROCCOLI*, PATRICIA A. MARTÍNEZ, EMILIANO J. DIMARCO, JUAN A. WAESSLE and OTTO C. WÖHLER
Instituto Nacional de Investigación y Desarrollo Pesquero (INIDEP), Paseo Victoria Ocampo Nº 1, Escollera Norte, B7602HSA -
Mar del Plata, Argentina. ORCID Gonzalo H. Troccoli https://orcid.org/0000-0002-0057-4325
INTRODUCTION
The Genus Dissostichus comprises two impor-
tant commercial species: D. mawsoni and D. elegi-
noides (Collins et al. 2010). The first one is dis-
tributed in Antarctic waters, while the second
reaches lower latitudes (Gon and Heemstra 1990).
Patagonian toothfish (D. eleginoides) has a wide
distribution in the southern hemisphere (Collins et
al. 2010; Nelson 2016), with its populations often
separated by vast expanses of deep ocean (Shaw et
al. 2004; Ashford et al. 2006; Rogers et al. 2006;
Ashford and Jones 2007). Patagonian toothfish is
a demersal species inhabiting shelves and slopes
of subantarctic islands of the Southern Ocean
(South Georgia Islands, South Sandwich Islands,
South Orkneys, Crozet, Kerguelen, Heard,
McDonald, Macquarie and Prince Edward, banks
such as Banzare, Ob and Lena, and regions of the
Ross Sea) and waters surrounding the southern
American cone, from Peru and Chile in the Pacific
Ocean to Argentina and Uruguay in the Atlantic
(Cousseau and Perrota 2004). The species inhabits
mainly the deep shelf, continental slope and sub-
marine canyons from 80 to 2,500 m depth (Prenski
and Almeyda 2000; Arkhipkin and Laptikhovsky
2010; Lee et al. 2021). Its ontogenetic cycle is
characterized by a pelagic behavior during early
development stages (eggs and larvae) (Evseenko
et al. 1995; North 2002) and a demersal behavior
from juvenile to adult. Several studies in the South
Atlantic (Agnew et al. 1999; Arkhipkin et al.
2003; Arkhipkin and Laptikhovsky 2010; Collins
et al. 2010; Péron et al. 2016; Lee et al. 2021) and
Indian Ocean (Duhamel 1981; Duhamel and
Pletikosic 1983; López Abellán 2005; Welsford et
al. 2011) have indicated a correlation between
larger fish and their distribution at greater depths.
This ontogenetic shift in habitat is common in
deep-sea fish (Agnew et al. 1999). However, spa-
tial segregation between individuals may also be
related to biological factors, such as trophic (Troc-
coli et al. 2020) or reproductive behavior (Brown
et al. 2013a; Boucher 2018) and environmental
variables, such as currents and their physical vari-
ables (Lee et al. 2021).
In the process of managing a fishing resource,
it is essential to be aware of the existence of uni-
tary stocks in order to determine whether a fish-
ery can be managed independently or integratedly
with other jurisdictions (Ying et al. 2011;
Hawkins et al. 2016; Kerr et al. 2017; Cadrin
2020). There are many factors contributing
knowledge about differentiation of stocks, such
as the understanding of fish movements in differ-
ent temporal and spatial scales (Brown et al.
2013a; Lee et al. 2022). The abundance of certain
populations may be subject to change in response
to any variation of relevant factors (Cianelli et al.
2013). The identity of the southwest Atlantic
toothfish stock (SA) has been the subject of vari-
ous studies. There is a well-documented genetic
differentiation between individuals from Patag-
onian shelf and those from South Georgia and
South Sandwich Islands (Shaw et al. 2004;
Rogers et al. 2006; Canales-Aguirre et al. 2018).
However, detailed population structure of the
species on the Argentine and Chilean Patagonian
shelf is still unknown. So far, genetic studies in
the area have not demonstrated any differentia-
tion justifying the presence of more than one pop-
ulation in the Chilean Pacific and Argentine
Atlantic (Shaw et al. 2004; Rogers et al. 2006;
Canales-Aguirre et al. 2018; Arkhipkin et al.
2022). Notwithstanding, other complementary
approaches, such as tag-recapture (Brown et al.
246 MARINE AND FISHERY SCIENCES 36 (3): 245-265 (2023)
presente trabajo, parece evidente que la especie en el cono sur americano carece de desplazamientos migratorios regulares que involu-
cren a una parte significativa del stock.
Palabras clave: Marcado, recaptura, caladero, stock.
2013a; Lee et al. 2022), otolith microchemistry
(Ashford et al. 2006, 2007; Ashford and Jones
2007), parasitology (Brickle et al. 2006; Brown et
al. 2013b), otolith shape (Lee et al. 2018), repro-
ductive characteristics (Laptikhovsky et al. 2006;
Pájaro et al. 2009; Boucher 2018) and oceano-
graphic modelling of dispersal patterns (Ashford
et al. 2012), indicate some heterogeneity along
the slope of the southern American cone, suggest-
ing the existence of different stocks in the area
(Wöhler et al. in press).
Tag-recapture programs established in differ-
ent fisheries around the world (Williams and
Lamb 2002; Williams et al. 2002; Marlow et al.
2003; Tuck et al. 2003; Agnew et al. 2006b; Dunn
et al. 2007; Roberts and Agnew 2008; Brown et
al. 2013a; Rubilar et al. 2013; Lee et al. 2022)
have been a very useful tool to understand the
geographic and bathymetric movements of fish,
contributing to understand fish growth, behavior
and population structure (Collins et al. 2010). The
so-called ‘conventional tags’ enable the determi-
nation of the distance traveled from the release
point to the recapture point, which can be corre-
lated with a specific timeframe. Specimens of the
Genus Dissostichus are suitable for tagging and
recovery studies as they are relatively robust and,
given the lack of a swim bladder, do not sustain
serious decompression injuries when captured
and brought to the surface from the depths in
which they inhabit (Agnew et al. 2006a). As a
result, numerous studies have investigated their
movement patterns through this approach
(Williams et al. 2002; Marlow et al. 2003; Tuck et
al. 2003; Agnew et al. 2006b; Roberts and Agnew
2008; Petrov and Tatarnikov 2010; Stacy et al.
2021; Lee et al. 2022; Grilly et al. 2022).
The Patagonian toothfish tag and recapture
program has been in place in Argentine waters
since 2004 to learn more about possible migrato-
ry movements of the species in the southwestern
Atlantic. This article analyzed results derived
from the aforementioned program as a contribu-
tion to our understanding of migratory move-
ments of the juvenile toothfish fraction and the
population structure present in the Argentine
Patagonian shelf.
MATERIALS AND METHODS
In 2004, researchers from the Instituto
Nacional de Investigación y Desarrollo Pesquero
(INIDEP) launched the Tag and Recapture Pro-
gram based on an experience conducted onboard
of a commercial longliner. Individuals were
tagged with an Australian-made standard anchor
T-bar tag (Hallprint, Adelaide), similar to the ones
used in various toothfish tagging programs at the
Commission for the Conservation of Antarctic
Marine Living Resources (CCAMLR). The Pro-
gram became a mandatory activity for fishing
vessels with an individual transferable quota fish-
ing for the species at the beginning of 2007. The
program focuses on specimens that have been
tagged in two sectors of the fishing ground of the
Argentine commercial fleet: one corresponding to
the northern Sector (NS), bordering the slope
between 37° S and 47° S, where the longline fleet
operates; and the other to the southern Sector
(SS), located to the east of De los Estados Island
(54° 30'S-55° 00'S and 64° 00'W-58° 00'W)
and south of Tierra del Fuego (55° 00'S-57° 30'
S and 67° 00'W-64° 00'W), which is visited by
both longliner and trawler fleets.
With the progressive withdrawal of longliners
as from 2017, specimens were only tagged in
research surveys conducted onboard of short-set
trawlers at shallower depths, contemplating a
conditioning time for the tagged fish in water
tanks before discarding those that did not recover
properly and therefore increase the survival rate
of those released. Fish were selected, prioritizing
those with the best general condition, measured
(cm) and weighed (g). Tags were inserted with a
gun on the left side of the dorsal part of the fish,
in the area of muscle between the second and
247
TROCCOLI ET AL.: MIGRATORY PATTERNS OF THE PATAGONIAN TOOTHFISH IN THE SOUTHWESTERN ATLANTIC OCEAN
third spine of the first dorsal fin (Figure 1). Data
on geographical position (longitude and latitude),
date and depth of the capture and subsequently
release sites were recorded. The release position
remained the same or very close to the one from
which the capture was obtained.
All tagged specimens were recaptured by com-
mercial fleets. When a tagged toothfish was
caught, observers onboard recorded its tag num-
ber, size, weight, and sex. Vessel operators
recorded data if no observer was present. Recap-
tures in Chilean waters were recorded by both
freezer and artisanal fleets. Observer records
included tag number, size, weight, sex, date, time,
depth, latitude, and longitude. In some cases, tags
were recovered after processing, leaving only the
date and position of recapture available.
Estimated traveled distances by specimens and
potential trajectories were visualized from tag and
recapture position data by using Google Earth v.
7.3.3 Pro. They were divided into four categories:
Short Distances (<20 nm), Short Intermediate Dis-
tances (20-120 nm), Long Intermediate Distances
(120-400 nm) and Long Distances (>400 nm).
Considering that toothfish is a deep-sea species, a
trajectory on the edge of the slope between the
release position and the recapture position was
assumed, and the minimum distances that the fish
would have traveled in nautical miles (1 nm =
1,852 km) were measured. Subsequently, displace-
ment of specimens was analyzed with a General-
ized Additive Model (GAM), using the ‘mgcv’
package of the R program version 4.3.0. These
models are an extension of general linear models
replacing the linear predictors with additive pre-
dictors through a smoothing function or spline
(Hastie and Tibshirani 1986; Wood 2006). Four
different transformations were tested on the
response variable (log, square root, cube root and
box cox) to reduce the spread of data. The log
transformation provided the best-validated model
fit. Continuous explanatory variables considered
influential in the traveled distance were the length
of tagged specimens (TL), the period of time
between the release and the capture (Days at liber-
ty DL), and the tagging Depth (D). Factors con-
sidered were the sector in which specimens were
tagged (northern and southern) and the season
(spring, summer, autumn and winter). The general
model was the following:
248 MARINE AND FISHERY SCIENCES 36 (3): 245-265 (2023)
Figure 1. Position of the body where the T-bar style tag was implanted. In some specimens two tags were implanted.
Log(Distance) =m+s(TL) +s(DL) +s(D) +Sector
+Season +Error
Family =Gaussian, Link =‘Identity’
where e~N (0, s2e). First, the existence of
collinearity between variables was verified to
eliminate any variable correlated with another
(Zuur et al. 2009). Once definitive variables were
obtained, the best model was chosen based on the
stepwise selection process according to the
Akaike Information Criteria and Generalized
Cross Validation (Akaike 1973; Burnham and
Anderson 2004; Wood 2012). In both cases, the
lower the value the better the model obtained will
be. In addition, the adjusted multiple determina-
tion coefficient was calculated for each model,
and the explanatory capacity of the model built
through the explained deviance was calculated.
Subsequently, influential points were eliminated,
obtaining the final model. Finally, its graphic val-
idation was carried out using the gam.chek func-
tion (‘mgcv’) and those variables significant to
the final model were plotted (Fernández Casal et
al. 2022).
RESULTS
A total of 5,907 toothfish have been tagged in
the northern Sector (NS) and southern Sector
(SS) since the beginning of the Program in 2004.
A total of 5,528 specimens were tagged onboard
the longline fleet and 379 on the trawler, from
which, 26.04% were tagged in the NS, while the
remaining 73.96% were tagged in the SS (Figure
2; Table 1). To date, a total of 121 specimens have
been recaptured, of which 25 (20.7%) were
recaptured in the NS, 84 (69.4%) in the SS, and
12 (9.9%) in Pacific waters off the Chilean coast
(Table 1; Figure 3). At the same time, 3 speci-
mens from Chilean waters and 2 tagged in the
249
TROCCOLI ET AL.: MIGRATORY PATTERNS OF THE PATAGONIAN TOOTHFISH IN THE SOUTHWESTERN ATLANTIC OCEAN
Figure 2. Release position of tagged toothfish specimens in the Argentine Exclusive Economic Zone (EEZ).
area corresponding to the Argentine Patagonian
shelf, around Malvinas Islands, were also recap-
tured in the SS. The majority of tagged specimens
in each year were juveniles in size (Figure 4).
Juvenile fish consisted of 75.18% of fish tagged
across the sample period, ranging from 53.75%
(2012) to 100% (2019).
From their release site, 67.5% were recaptured
at a distance of less than 20 nm, while 15% trav-
eled short intermediate distances less than
120 nm. The smaller fraction (5%) covered dis-
tances between 120 and 400 nm (longer interme-
diate distances) and 12.5% were recaptured at
greater distances (more than 400 nm) from their
tagging locations. Only 9.9% of the fish left the
Argentine fishing ground. Most of specimens
(87.5%) covered distances of under 400 nm,
remaining inside the same sector, whose length
was estimated to be around 370 nm for both sec-
tors. In the NS, 83% (25) of tagged specimens
moved within 400 nm. Seventy-seven percent of
them (23) were even recaptured at less than 20
nm. Only 17% (5) of the total was recaptured at
distances greater than 400 nm, exceeding the lim-
its of that sector of the Argentine fishing ground.
In the SS, 89% (81) of the fish moved less than
400 nm from their release site, and 64% of the
total (58) moved less than 20 nm. The remaining
250 MARINE AND FISHERY SCIENCES 36 (3): 245-265 (2023)
Table 1. Number and percentage of toothfish specimens tagged and recaptured in the northern, southern, and Pacific Ocean sec-
tors, indicating recapture rate per year (%).
Tagged Recaptured
Year Northern Southern Northern Northern Pacific Percentage
2004 247 247 0 0 0 0.00
2005 0 0 0 0 1 0.00
2006 0 0 0 0 0 0.00
2007 14 763 0 0 0 0.00
2008 300 755 4 3 0 0.66
2009 368 685 4 5 0 0.85
2010 223 705 2 23 2 2.91
2011 37 465 1 23 1 4.98
2012 99 154 9 13 1 9.09
2013 92 244 1 4 4 2.68
2014 0 0 0 2 0 0.00
2015 0 0 2 2 0 0.00
2016 0 0 2 2 0 0.00
2017 28 32 0 1 2 5.00
2018 130 223 0 3 0 0.85
2019 0 40 0 2 1 7.50
2020 0 56 0 1 0 1.79
Total 1,538 4,369 25 84 12 2.05
Percentage 26.04 73.96 20.66 69.42 9.92
11% (10 fish) were recaptured at a distance
greater than 400 nm from the release site (Figure
5). The predominance of short distances traveled
after being tagged and released demonstrates the
affinity of the species for its residence sites in the
NS and SS of the Argentine fishing ground.
There was no clearly defined direction pattern
observed in the fish tagged in the NS (Figure 6).
Most of the specimens exhibited a distinct pattern
of movement towards the southeast and east.
However, one specimen that traveled a moderate
distance went in the opposite direction towards
the northeast. Furthermore, the specimens that
traveled the greatest distances all moved towards
the south. Only five of the recaptured fish crossed
the NS of the Argentine fishing ground, migrating
over long distances (up to approximately 1,500
nm), three of which were recaptured near the
Namuncurá/Burdwood Bank, and the rest in
southern Chile (Figure 7). A unified directional
movement was also not observed for fish tagged
and recaptured in the SS of the Argentine fishing
ground (Figure 8). Both westward and eastward
directions were observed for fish undertaking
movements less than 100 nm. Those that moved
greater distances did essentially to the west-
northwest (Figure 9). Regarding specimens
tagged in the SS, 11 of them exceeded the limits
of the Argentine fishing ground, eight of which
traveled distances in the direction of central-north
Chile, between 477 nm (885 km) and 2,100 nm
(3,889 km). The vast majority of the tagged fish
(64%) remained close to their release sites. A sin-
gle specimen was reported to the east, tagged at
54° 53' S-59° 08'W and caught at 55° 00' S-57°
37' W by the longliner ‘CFL Hunter in waters
near the Malvinas Islands (Martínez, unpublished
data).
The variables Days at liberty, Sector, and Sea-
son of tagging influenced on the traveled distance
in GAM results (Table 2). The final model was
defined by these three variables, which explained
34.4% of the variability of the model. The length
of fish at the time of tagging and the depth of
release were not significant in the movements of
toothfish. This hypothesis and the homogeneity
of variances seems to be adequate from validation
graphs for normality (Figure 10).
251
TROCCOLI ET AL.: MIGRATORY PATTERNS OF THE PATAGONIAN TOOTHFISH IN THE SOUTHWESTERN ATLANTIC OCEAN
Figure 3. Reported recapture positions of tagged toothfish specimens in the Argentine Exclusive Economic Zone (EEZ).
252 MARINE AND FISHERY SCIENCES 36 (3): 245-265 (2023)
Figure 4. Distribution of relative frequencies of grouped lengths of tagged toothfish specimens per year. The black dotted line
represents the length of first maturity estimated at 82 cm (Pájaro et al. 2009).
2018 2019 2020
2012 2013 2017
2009 2010 2011
2004 2007 2008
25 50 75 100 125 25 50 75 100 125 25 50 75 100 125
0.00
0.02
0.04
0.06
0.00
0.02
0.04
0.06
0.00
0.02
0.04
0.06
0.00
0.02
0.04
0.06
Total length (cm)
Relative frecuency
Figure 5. Ratio of recaptured toothfish specimens based on the range of distance traveled in the northern and southern Sector.
0-20 20-120 120-400 >400
Northern Southern
Traveled distance range (nm)
Ratio
0.0
0.2
0.4
0.6
0.8
1.0
253
TROCCOLI ET AL.: MIGRATORY PATTERNS OF THE PATAGONIAN TOOTHFISH IN THE SOUTHWESTERN ATLANTIC OCEAN
Figure 7. Possible migratory route of specimens tagged in the northern Sector of the Argentine fishing ground and recaptured
more than 400 nm away from it. Orange circles indicate the tagging position and yellow ones the recapture position. The
five specimens that traveled long distances did so in a southerly direction.
Figure 6. Migratory movements corresponding to distances of less than 400 nm in the northern Sector of the Argentine fishing
ground.