Journal of the Marine Biological Association of the United Kingdom, 2008, 88(1), 183 –187.
doi:10.1017/S0025315408000106 Printed in the United Kingdom
#2008 Marine Biological Association of the United Kingdom
Diet of Tetrapturus belone (Istiophoridae) in
the central Mediterranean Sea
luca castriota1, maria grazia finoia2, silvana campagnuolo1, teresa romeo3,
antonio potoschi4 and franco andaloro1
1
Central Institute for Marine Research (ICRAM), STS Palermo, via Emerico Amari 124, 90139 Palermo, Italy, 2ICRAM, via di
Casalotti 300, 00166 Roma, Italy, 3ICRAM, STS Palermo Laboratorio di Milazzo, via dei Mille 44, 98057, Milazzo (Me), Italy,
4
Dipartimento di Biologia Animale ed Ecologia Marina, Università di Messina, Salita Sperone, S. Agata, 98166 Messina, Italy
The stomach contents of 69 Mediterranean spearfish Tetrapturus belone collected in the Strait of Messina, central
Mediterranean Sea were examined. Of the total specimens, caught by harpoon, only three stomachs were empty. Their
diet consisted mainly of pelagic fish and cephalopods. The most important piscine prey belonged to the families of
Belonidae, Clupeidae and Scomberesocidae. Cephalopods were mainly represented by Tremoctopus violaceus in terms of
per cent weight and by Illex coindetii in terms of per cent frequency of occurrence. Tetrapturus belone is an active predator
on epipelagic fast-moving prey and school-forming species. Its ecological role is similar to that of other large pelagic species
which share the same environment.
Keywords: billfish, diet, Mediterranean Sea, Strait of Messina, feeding habits, Tetrapturus belone
Submitted 21 September 2006; accepted 2 November 2007
INTRODUCTION
The Mediterranean spearfish Tetrapturus belone (Rafinesque)
is a pelagic species belonging to the family Istiophoridae. It is
considered a highly migratory species (Nakamura, 1985)
whose distribution is limited to the Mediterranean Sea,
although some specimens have been recorded from the
Atlantic side of the Strait of Gibraltar (Di Natale et al.,
2005b). Like other billfish, this species probably swims
in the upper 200 m water layer, generally above or within
the thermocline (Nakamura, 1985). It is considerably
abundant around Italy (Nakamura, 1985), particularly in the
Tyrrhenian Sea, where it is caught as by-catch of large
pelagic fisheries and in the Strait of Messina where it represents a target species (Di Natale et al., 2003). There, the
Mediterranean spearfish is fished at the surface by harpoons
with traditional boats called ‘feluche’ or ‘passerelle’, typically
used to catch swordfish, Xiphias gladius L., only from late
spring to summer. After the crisis in swordfish fishery of
the last years, worsened by the European ban of driftnets
since 2002 (UE Regulation no. 1239/98), the interest for the
Mediterranean spearfish fishery is increasing, despite its
lower commercial value when compared to that of swordfish.
In the last decades, the catches by harpoon of this species in
the Strait of Messina showed an increasing trend, from
39 kg total weight in 1976 to 1221.5 kg in 2003 (Di Natale
et al., 2005a).
Although the importance of this species is rising on the
market, scanty information on its biology and ecology is available. Robins & De Sylva (1960, 1963) and Spartà (1953, 1961)
studied its eggs and larval development; Cavaliere (1962) and
Corresponding author:
L. Castriota
Email: castriotaluca@hotmail.com
Potoschi (2000) reported a few data on the biology and fishery
of the species in the Strait of Messina while catches from
Italian seas are reported by Di Natale et al. (2003, 2005a, b).
Some fishery and biological information are reported by De
Sylva (1975) and by Nakamura (1985). Feeding ecology is
an important aspect of the life-history strategy of fish and
may be a precious tool for the comprehension of trophic
dynamics and for the development of appropriate fishery
management strategies. However, in the case of the
Mediterranean spearfish, feeding ecology has been very
poorly investigated. Based on the examination of stomach
contents from a few specimens, a diet consisting of epipelagic
organisms is reported (Spartà, 1961; Bini, 1968; Tortonese,
1975; Nakamura, 1985).
As information about feeding of T. belone is still based on
feeble, sometimes doubtful observations, in this paper we aim
at describing its feeding habits in order to increase the knowledge of the biology of this scarcely studied species.
MATERIALS AND METHODS
The study of feeding habits was carried out on the stomach
contents of 69 Mediterranean spearfish, caught at the
surface by harpoons. Samples were collected from 1995 to
2004 in the Strait of Messina (Figure 1) at day-time, during
the fishing season for swordfish and Mediterranean spearfish
by harpoon, from late spring to summer.
Specimens were measured to the nearest cm from the tip
of the bill (upper jaw) to the posterior margin of the middle
caudal rays (LF); total weight (W ) was also recorded to the
nearest hectogram. The stomachs were removed and preserved in a 10% seawater –formalin solution for 24 h, and
then transferred to 80% alcohol for subsequent analysis of
contents. In the laboratory prey items were identified to the
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luca castriota et al.
Fig. 2. Length – frequency distribution of Tetrapturus belone from the Strait of
Messina sampled for stomach contents analysis.
Fig. 1. Map showing the sampling area of Tetrapturus belone in the central
Mediterranean Sea.
lowest possible taxonomic level, then counted and weighed to
the nearest milligram. As hard parts resistant to digestion (i.e.
cephalopod beaks) cumulate in the stomachs over more meals,
leading to overestimation of the importance of prey they
belong to, only prey bearing fleshy remains were considered
for the analyses, as they were likely to have been recently
eaten by the predator (see Santos et al., 2001). Cephalopod
beak lengths—the lower rostral length and the lower hood
length in decapods and octopods respectively (Clarke,
1986)—were used to estimate mantle length of digested cephalopods and to reconstitute their weights, using relationships
either in the literature (Clarke, 1986; Bello, 1991), or from
measurements on specimens in our reference collection
(ICRAM collection).
To assess the adequacy of the number of samples analysed,
the cumulative number of new prey types against the cumulative number of non-empty stomachs were plotted (Ferry
& Caillet, 1996). The PRIMER software was utilized to
compute a prey species accumulation plot as an average of
999 curves based on different random orders of the stomachs.
In order to assess whether the curve reached an asymptote, the
logistic and linear regressions were calculated and their goodness of fit coefficients R2 were compared: the sample size was
considered sufficient if the R2 for the logistic curve was higher
than the R2 for the linear relation (Castriota et al., 2005).
The importance of the different prey items was evaluated
by calculating the frequency of occurrence (%F ¼ number of
stomachs containing prey i/total number of stomachs
containing prey 100), abundance (%N ¼ number of prey
i/total number of prey 100) and reconstituted weight
(%W ¼ weight of prey i/total weight of all prey 100).
These values were used to calculate the index of relative
importance (IRI) for each taxonomic category using mass
instead of volume: IRI ¼ (%N þ %W ) (%F ) (Hyslop,
1980; Hacunda, 1981). Fullness index (IF ¼ no. stomachs
with food/ no. total stomachs) was also calculated.
The degree of diet specialization was given by the Levin’s
standardized index (Hurlbert, 1978; Krebs, 1989), Bi ¼
[(Sjp2ij)21 2 1] (n 2 1)21 where:
Bi ¼ Levin’s standardized index for predator i;
pij ¼ proportion of diet of predator i that is made up of prey j;
n ¼ number of prey items.
This index ranges from 0 to 1; low values indicate diets
dominated by few prey items (specialist predators), high
values indicate generalist diets (Krebs, 1989).
The binomial test was applied on the frequency of occurrence values of each prey category to select prevailing items
in the diet of Tetrapturus belone: a prey category was considered as rare if its frequency of occurrence was significantly
less than 5%, for P , 0.05. The binomial test was also repeated
on the abundance values of each prey category.
RESULTS
Mediterranean spearfish caught had an average total weight of
11.0 kg (range 2.8 – 22.0 kg) and an average fork length of
149 cm (range 89 –191 cm). Of the total stomachs examined
only three were empty, thus the fullness index was 0.96.
Figure 2 shows the length – frequency distribution of the
69 specimens used for the stomach contents analysis.
The cumulative prey types curve (Figure 3) for the entire data
set resulted as fitting better with a logistic curve (R2 ¼ 0.97;
F(1,64) ¼ 1627.2, P , 0.001) than with a linear relation (R2 ¼
0.92, F(1,64) ¼ 734.2; P , 0.001); therefore the sample size was
considered sufficient to describe the diet of Tetrapturus belone.
The analysis of the stomach contents led to the identification of 27 prey items (Table 1), belonging to two main
taxa: Pisces and Cephalopoda. A total of 421 fish, 59 cephalopods and 8 other invertebrates were found in the stomachs
analysed, with a mean of 7.4 prey individuals (+ 0.6 SE)
per stomach.
Fig. 3. Prey species accumulation plot as an average of 999 curves based on
different random orders of the stomachs extracted (number of stomachs ¼ 66).
Vertical bars represent standard deviation.
diet of tetrapturus belone in mediterranean
Table 1. Percent frequency of occurrence (%F), percent of total number
(%N), percent of total weight (%W), index of relative importance (IRI) and
percent index of relative importance (%IRI) for food items of Tetrapturus
belone.
%IRI
Prey Categories
%F
%N
%W
Pisces unid.
Belonidae
Belonidae unid.
Belone belone
Belone svetovidovi
Carangidae
Seriola dumerili juv.
Trachurus sp.
Centriscidae
Macroramphosus scolopax juv.
Clupeidae
Clupeidae unid.
Alosa sp.
Sardina pilchardus
Sardinella aurita
Coryphaenidae
Coryphaena hippurus juv.
Engraulididae
Engraulis encrasicolus
Gobiidae
Scomberesocidae
Scomberesox saurus
Scombridae
Sparidae
Oblada melanura
TOTAL PISCES
Cephalopoda unid.
Octopoda
Tremoctopus violaceus
Teuthoidea
Ancistrocheirus lesueuri
Histioteuthis bonnellii
Illex coindetii
Todarodes sagittatus
TOTAL CEPHALOPODS
Invertebrates unid.
Tunicata Salpida
Siphonophora Diphyidae
43.9
30.7
4.3
1538.6
36.8
6.1
33.3
1.5
3.3
21.1
0.2
1.3
20.5
0.1
27.6
1388.4
0.4
0.7
33.2
,0.1
1.5
3.0
0.2
1.2
0.2
0.5
0.6
5.2
,0.1
0.1
6.1
4.5
0.1
27.9
0.7
4.5
4.5
1.5
16.7
4.7
1.0
0.2
6.4
0.6
0.8
,0.1
12.3
24.4
8.3
0.3
310.4
0.6
0.2
,0.1
7.4
1.5
0.2
0.6
1.2
,0.1
3.0
1.5
1.0
0.8
0.1
,0.1
3.5
1.3
0.1
,0.1
18.2
3.0
9.8
0.6
10.6
0.1
372.3
2.0
8.9
,0.1
IRI
1.5
0.2
0.1
0.5 ,0.1
97.0 86.3 52.2 13435.1 87.1
10.6
3.7
0.2
41.0
1.0
1.5
0.2 ,0.1
0.3 ,0.1
7.6
2.7 43.7
351.3
8.4
4.5
0.8
0.9
4.5
1.0
0.3
10.6
3.1
1.7
3.0
0.6
1.0
33.3 12.1 47.7
3.0
0.4 ,0.1
1.5
0.2 ,0.1
1.5
1.0 ,0.1
7.9
0.2
5.9
0.1
50.7
1.2
4.7
0.1
1992.3 12.9
1.3 ,0.1
0.3 ,0.1
1.6 ,0.1
Fish were the dominant group according to all numerical
indicators and were mostly composed of pelagic species.
Ten families were identified among them, with the dominance
of Belonidae which represented 41.2% of the total preyed fish
in terms of %IRI. The families Clupeidae and Scomberesocidae
were also well represented (%IRI ¼ 12.9 and 8.7 of the total
preyed fish respectively). The species Belone belone (L.),
Scomberesox saurus (Walbaum) and Sardinella aurita
Valenciennes played the major role in the feeding of
Mediterranean spearfish (Table 1).
Cephalopods occurred in 33.3% of the stomachs analysed
and accounted for 12.1% in number, and 47.7% in weight of
the total preyed organisms. Cephalopod remains were attributed to 5 species, all pelagic. Tremoctopus violaceus Delle
Chiaje was the most important species among them in
terms of %W, while Illex coindetii (Verany) was the most
represented in terms of %F.
Levin’s standardized index, calculated for the evaluation of
diet breadth, was 0.2 for the numerical abundance and 0.1 for
the biomass of the prey items.
The results of the binomial test indicated Belonidae,
Clupeidae, Scomberesocidae and Teuthoidea as the significantly non-rare prey categories in terms of frequency
of occurrence. The same results were obtained in terms of
abundance except for Teuthoidea which were at the limit of
significance (P ¼ 0.05).
DISCUSSION
Very few studies have been carried out on the biology of the
Mediterranean spearfish and none on its feeding habits.
Based on examination of stomach contents from a few specimens, some authors propose that it probably feeds on pelagic
fish, such as sardines (Clupeidae), flyingfish (Exocoetidae),
carangids, scombrids, dolphinfish (Coriphaenidae) and,
around Sicily, Atlantic sauries, sardine-like fish, needlefish
and pilotfish (Bini, 1968; De Sylva, 1975; Tortonese, 1975;
Nakamura, 1985). Partial teuthophagy is also reported in the
Ligurian Sea (Garibaldi & Orsi Relini, 2005). Diet preference
of Tetrapturus belone for pelagic fish would justify occasionally catches with surrounding nets used for the fishery of the
Atlantic saury in the Strait of Messina (Cavaliere, 1962;
Spartà, 1961; Tortonese 1975).
Our results confirmed fish as the main prey of the
Mediterranean spearfish, although cephalopods were also
well represented in terms of frequency of occurrence and
reconstituted weight (Figure 4). If we also consider the large
numbers of accumulated beaks in most stomachs examined,
the frequency of occurrence of cephalopods increases from
33.3% to 58.2% and their abundance rises to 41.8%, confirming their important role in the diet of T. belone. Looking at
the diets of other pelagic predators, cephalopods seem to
play a most important part as food of the Atlantic white
marlin T. albidus Poey, a very close congener of T. belone,
also known from the Mediterranean Sea (Nakamura, 1985).
They are also preyed upon by large predacious fish such as
tunas, swordfish, sharks and other billfish (Roper et al.,
1984; Bello, 1990, 1991, 1999; Abitı́a-Cárdenas et al., 2002;
Rosas-Alayola et al., 2002; Vaske et al., 2004).
The most represented fish species in the diet of T. belone
(i.e. Belone belone, Scomberesox saurus and Sardinella
aurita) are widely distributed in the Strait of Messina
(Spartà, 1961); they used to form large schools that would
allow the Mediterranean spearfish to maximize the efficiency
of predation. Billfish require large amounts of energy to
survive and coming across schools of fish or cephalopods
Fig. 4. Frequency of occurrence (%F), abundance (%N) and biomass (%W) of
main prey categories (tel ¼ unidentified teleosts; bel ¼ Belonidae; sco ¼
Scomberesocidae; clu ¼ Clupeidae; oct ¼ Octopoda; teu ¼ Teuthoidea) in
the diet of Tetrapturus belone from the Strait of Messina. Dashed lines refer
to total fish (left) and total cephalopods (right).
185
186
luca castriota et al.
helps them in providing the large rations necessary to support
their high metabolic demands. This chasing strategy has been
also observed in other billfish as well as in other pelagic predators (Abitı́a-Cárdenas et al., 2002).
Other prey found in the stomachs of T. belone, such as
juvenile Macroramphosus scolopax (L.), carangids, juvenile
dolphinfish, sparids, juvenile scombrids, juvenile gobiids and
European anchovies, may be considered as secondary or accidental prey, at least in the sampling period; all grouped, they
accounted for only 1.7% in weight and 8.8% in number. All
preyed specimens were epipelagic organisms, also including
juveniles of demersal or benthic fish which spend their early
life stages in the upper waters.
Overall, according to the prey species composition found,
T. belone pursues epipelagic prey. As confirmed by the low
Levin’s index, few species accounted for most of the prey consumed, indicating specialist feeding at least in the sampling
period, which was limited to summer months. This result is
atypical for billfish which are usually referred to as generalists
(Somvanshi & Varghese, 2001; Abitı́a-Cárdenas et al., 2002;
Vaske et al., 2004). Resource composition and prey turn-over
in the area over the short sampling period may explain this
result. Some species such as Coryphaena hippurus L. and
Naucrates ductor (L.), which are reported as prey of
T. belone (Nakamura, 1985), were scarcely represented or
absent in the stomachs of the Mediterranean spearfish from
the Strait of Messina. These two species do increase in abundance in Sicilian waters from August to December (Andaloro
et al., 2003), when the swordfish fishing season by harpoon is
about to finish.
According to De Sylva (1975), the Mediterranean spearfish,
like other billfish, is typically a clear-water species, requiring
high transparency waters for its feeding which is largely
visual. Diurnal feeding is also reported for other istiophorids,
albeit it may extend till night-time depending on moon phases
(Trias et al., 1996). However, in the stomachs of T. belone
from the Strait of Messina, we have found highly digested
bodies and hard part remains of cephalopods. These organisms are known to undergo diel vertical migrations, wherein
they commonly inhabit deep water during the day, then
ascend towards the surface at night (Roper, 1974). Hence,
their high occurrence and abundance and the condition of
their remains in the stomachs of specimens caught at
day-time suggest that they were probably ingested the night
before the Mediterranean spearfish capture, thus revealing
potential nocturnal predatory behaviour. As cephalopods are
predators upon mesopelagic organisms (Sanchez, 1982;
Marabello et al., 1996), they represent, in terms of trophic
webs and energetic fluxes, a major link between mesopelagic
and epipelagic environments.
Generally, T. belone is presumed to feed upon organisms
whose distribution is closely determined by oceanographic
and trophic conditions: organisms concentrated at or just
above the thermocline (De Sylva, 1975) as well as those
moving upward for trophic reasons should be expected to
attract this predator for feeding purposes. In the Strait of
Messina, T. belone shares the habitat with other large
pelagic predators, mainly the bluefin tuna Thunnus thynnus
(L.), the swordfish X. gladius and the dolphinfish C. hippurus
(Romeo et al., 2001), as confirmed by catch records by
harpoon fishery over about three decades, from 1976 to
2003 (Di Natale et al., 2005a). Their concentration in this
area, as well as that of T. belone, is possibly due to the
considerable upwelling of food and nutrients into the upper
layers of the Strait. Thus, they may be considered potential
competitors for food, although they possibly adopt different
strategies for exploiting the same environment (Dagorn
et al., 2000).
ACKNOWLEDGEMENTS
The authors are grateful to V. Esposito for the analysis with
PRIMER, to M. Falautano and anonymous referees for their
constructive criticisms, and to P. Perzia for technical support.
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Correspondence should be addressed to:
Luca Castriota
Central Institute for Marine Research (ICRAM)
STS Palermo
via Emerico Amari 124
90139 Palermo
Italy
castriotaluca@hotmail.com
Romeo T., Ancora S., Manganaro A., Andaloro F. and Fossi C. (2001)
The swordfish fishing by harpoon in the Strait of Messina. Rapports de
la Commission Internationale pour l’Exploration Scientifique de la Mer
Méditerranée 36, 318.
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