Parasitol Res (2009) 105:1637–1642
DOI 10.1007/s00436-009-1604-9
ORIGINAL PAPER
Abnormalities on cephalic hooklets of advanced third-stage
larvae from Gnathostoma Owen, 1836 (Nematoda:
Gnathostomidae) collected from Mexican rivulus
Millerichthys robustus Costa, 1995 (Ciprinodontiformes:
Rivulidae) in Tlacotalpan, Veracruz, Mexico
Miguel Ángel Mosqueda-Cabrera &
Angélica Ocampo-Jaimes
Received: 7 January 2009 / Accepted: 14 August 2009 / Published online: 3 September 2009
# Springer-Verlag 2009
Abstract Morphological abnormalities were observed on
the cephalic bulb hooklets of advanced third-stage larvae
(AdvL3) of genus Gnathostoma. The larvae were obtained
from the fish “Mexican rivulus” Millerichthys robustus
collected from a seasonal pond near Tlacotalpan, Veracruz,
Mexico. The abnormalities involved (1) extra rudimentary
hooklets, located between the four rows and after the fourth
row, (2) branched or lobulated hooklets, and (3) fragmented
hooklets not uniformly disposed in rows. The alterations
observed on the cephalic bulb hooklets do not represent
intraspecific variations, and they may be considered as a
potential tool for assessing the presence of pollutants or
stressors located within the ecosystem.
Introduction
Because of their morphoanatomy, importance for human
and animal health, and unique life cycle (which includes at
least three hosts) gnathostomes are interesting. In this sense,
the first intermediate host is a cyclopoid copepod, where an
early third-stage larva (EaL3) develops. Commonly, the
second intermediate host is a fish, where the advanced
third-stage larva (AdvL3) develops. The definitive host is a
carnivore mammal, where the larva completes its developM. Á. Mosqueda-Cabrera (*) : A. Ocampo-Jaimes
Departamento El Hombre y su Ambiente,
Universidad Autónoma Metropolitana-Xochimilco,
Calzada del Hueso No. 1100, Col. Villa Quietud,
Delegación Coyoacán,
04960 México, D. F., México
e-mail: zitzitl@correo.xoc.uam.mx
ment to the adult stage (Almeyda-Artigas et al. 2000;
Miyazaki 1954 and 1960). In Mexico, the three species of
Gnathostoma have been documented (i.e., G. binucleatum
Almeyda-Artigas 1991, G. turgidum Lamothe-Argumedo et
al. 1998, and G. lamothei Bertoni-Ruiz et al. 2005). The
identification of AdvL3 of these species is important
because of their possible participation as causative agents
of the human disease called gnathostomiasis.
According to Miyazaki (1960) some of the most useful
criteria to differentiate the AdvL3 of the genus Gnathostoma
are: (1) number of transverse rows of hooklets in the cephalic
bulb and (2) quantity, shape, and size of the hooklets
occurring in each row. Consequently, the study of the shape
of the hooklets in the cephalic bulb has been utilized as a
criterion for differentiating species. In this sense, Akahane et
al. (1995) documented for the first time, abnormalities of the
cephalic hooklets in larvae of the genus Gnathostoma. They
observed a new kind of AdvL3 taking into account the shape
of the hooklet which shows a ramified base (zigzag shape).
On the other hand, two studies have documented morphological variations or abnormalities of the cephalic bulb
hooklets of AdvL3 from G. spinigerum. The first, carried
out by Rojekittikhun and Pubampen (1998), recorded that
15.5% of the larvae isolated from the liver of mice
experimentally infected showed morphological variations or
abnormalities. The most common variations were additional
rudimentary hooklets after the fourth row and between the
four rows of the cephalic bulb (10.8%). They concluded that
the variations were due to intraspecific differences. The
second study, by Rojekittikhun et al. (1998) about larvae
isolated from the viscera of eels Fluta alba bought at a
Bangkok marketplace, showed a higher percentage of
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Parasitol Res (2009) 105:1637–1642
morphological variations and abnormalities (25.4%).
Such variations were considered as interspecific differences
by these authors. Recently, Martínez-Salazar and LeónRègagnon (2005) have reported the intraspecific variability
of AdvL3 G. binucleatum from freshwater fishes in Tres
Palos Lagoon, Guerrero, Mexico. They documented hooklets
additional to those of the regular rows of the cephalic bulb
(8.6%). In the current study, we record the presence of
AdvL3 from Gnathostoma in a naturally infected Mexican
rivulus Millerichthys robustus as well as the abnormalities
observed in the cephalic bulb hooklets.
Fig. 1 Male M. robustus. Scale bar 10 mm
Materials and methods
Results
Sampling was carried out near Tlacotalpan, Veracruz Mexico.
The host M. robustus (Ciprinodontiformes: Rivulidae; Fig. 1)
were collected from “El Tamarindo”, a drying seasonal pond
(18°37′39.3″N, 95°38′53.0″W), using spoon-like nets. The
host M. robustus is an annual fish (term applied to species
living in seasonal freshwater biotopes) that inhabits the
Papaloapan and Coatzacoalcos Rivers in Mexico (Costa
1995). This species is endemic to Mexico and according to
the Mexican regulations (NOM-059-Ecol-2001), it is considered an “endangered species” (Diario Oficial de la
Federación 2002). In order to harvest every larva, the fish
were taken alive to the laboratory, where they were killed
and digested with artificial gastric juice (7 g pepsin in 10 ml
HCL/1,000 distilled water) during 4 h at 40°C. On the other
hand, “guavinos” Gobiomorus dormitor (Pisces: Eloetridae)
were collected from the Papaloapan River, near the town of
Tlacotalpan (18°36′N, 95°39′W) using a net or a hook; once
in the laboratory, a meticulous examination of the musculature was carried out. All larvae were fixed in hot 70%
ethanol, cleared in Amann lactofenol for their study in
temporary wet mounts on glass slides, and later stored in
70% ethanol. A light microscope was used for the study. All
measurements are given in micrometers, unless otherwise
stated, and they are presented as a range, followed by the
mean±standard deviation in parentheses. Photomicrographs
were obtained by using a Kodak Technical Pan black and
white film. Specimens were deposited in the “Colección
Helmintológica de la Universidad Autónoma Metropolitana
Unidad Xochimilco (CHUAMX), D. F., México”; accession
numbers are: CHUAMX-G017 for eight AdvL3 obtained
from M. robustus from “El Tamarindo” (1995); CHUAMXG036 for four AdvL3 obtained from M. robustus from “El
Tamarindo” (1998); and CHUAMX-G038 for 30 AdvL3
obtained from G. dormitor from Papaloapan River (1998).
The hosts G. dormitor and M. robustus were identified
according to Espinosa-Pérez et al. (1993) and Costa (1995),
respectively. The infection parameters utilized are those
proposed by Bush et al. (1997).
Three collections were performed, one in October 1995 and
two in February 1998. A total of 80M. robustus were
collected at the studied pond in 1995, from which eight
larvae were recovered and later examined. During 1998, 30
M. robustus collected from the same pond were examined
and four larvae were obtained; additionally, 14 guavinos
were examined from the Papaloapan River, five of them
were infected and 13 AdvL3 were recovered.
Comparison between measurements of larvae obtained
from different hosts in 1995 and 1998 are shown in
Table 1. In the larvae collected from M. robustus in 1995,
two types of morphological variations and abnormalities
of the cephalic hooklets were observed, that is, extra
rudimentary hooklets below the fourth row (75%) or
between the four rows of hooklets and lobulated or
branched hooklets (25%; Fig. 2a). The measurements of
the larvae collected in 1998 were not different from those
of 1995, but the alterations of the cephalic bulb hooklets
were more evident. All larvae showed fragmented hooklets not uniformly disposed in the rows, and without a
point. This made it impossible to count the number of
cephalic hooklets (Fig. 2b, c). The AdvL3 isolated from
guavinos did not show cephalic hook alterations (Fig. 2d)
and are similar to those described by Almeyda-Artigas et
al. (1994) as G. binucleatum.
The parasite abundance in M. robustus was 0.10 and
0.13 for collections of 1995 and 1998, respectively, and
because of the method utilized for recovering the larvae, it
was not possible to calculate other infection parameters. In
the case of the larvae from G. dormitor, the prevalence was
about 36%, the intensity was from 1 to 8, the mean
intensity was 2.6, and the abundance was 0.93.
Discussion
The AdvL3 from every host species were slightly different
in sizes. The largest were those isolated from G. dormitor;
Parasitol Res (2009) 105:1637–1642
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Table 1 AdvL3 of Gnathostoma, naturally obtained from hosts collected in the Papaloapan River and seasonal ponds near the town of
Tlacotalpan, Veracruz, Mexico
Observation
Gnathostoma sp.a
Gnathostoma sp.a
G. binucleatumb
Total length
Maximum width
Esophagus length
Esophagus width
Cephalic bulb length
Cephalic bulb width
Location of cervical papillae
Location of excretory pore
Number of hooklet rows in the
body
I
II
III
IV
IV-I
N
2,792.0–4,276.8
202.5–226.8
1,109.7–1,239.3
147.2–171.7
78.0–106.8
178.6–192.9
12–15
16–25
170–283
3,097.2–3,760.0 (3,356.3±445.3)
203.7–220.0 (211.1±18.6)
ND
ND
74.4–112.8 (86.1±12.8)
155.2–190 (171.7±9.1)
10–15 (12.4±1.4)
22–28 (25.2±2.4)
235–250 (240.5±20.2)
2,300.4–4,338.3
243.0–348.3
850.5–1,490.4
102.2–298.4
73.9–180.7
149.9–262.8
10–17
27–35
222–303
(3,799.6±433.7)
(220.1±10.8)
(1,170.4±54.9)
(161.5±8.9)
(85.8±10.12)
(183.7±6.1)
(13.3±1.3)
(21.0±2.1)
(250. 3±26.4)
36–40 (38±1.9)
39–45 (42.3±2.4)
39–46 (43.0±2.8)
48–52 (49.8±1.6)
10–15 (11.8±1.7)
8
4
(3,143.5±669.6)
(317.7±26.3)
(1,198.4±155.7)
(178.5±43.0)
(139.4±27.2)
(220.1±26.4)
(13.5±2.0)
(30.0±2.3)
(259.1±21.8)
36–44 (40.2±2.3)
35–47 (43.5±2.7)
39–51 (46.9±2.6)
44–54 (49.9±2.5)
4–16 (9.6±2.7)
13
ND not determined
a
Obtained from M. robustus collected from “El Tamarindo” (1995 and 1998, respectively)
b
Obtained from guavino G. dormitor collected from Papaloapan River (1998)
which might be attributed to a larger muscular space
available for the development of the larvae and/or to the
longevity of the host. The number of hooklets in the rows
of the cephalic bulb is similar to that reported for G.
binucleatum and G. spinigerum (Table 2). The most
important difference between G. binucleatum and G.
spinigerum (absent in America according to AlmeydaFig. 2 Front view of cephalic
bulbs of AdvL3 of Gnathostoma. a Larva from M. robustus
collected in 1995, with abnormal hooklets. b–c Larva from
M. robustus collected in 1998,
with abnormal hooklets. d Larva
of G. binucleatum from G. dormitor, with four rows of normal
hooklets. Scale bar 50 μm
Artigas et al. 2000) appears to be the average number of
hooklets appearing in every row; G. spinigerum presents,
on average, four hooklets more than G. binucleatum in all
the rows, a peculiarity that was previously documented by
Akahane et al. (1994). In the case of G. binucleatum, no
more than 50 hooklets are observed in the second and third
rows, as frequently occurring in G. spinigerum (Table 2).
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Parasitol Res (2009) 105:1637–1642
Table 2 Comparisons of number of hooklets in the four rows of the cephalic bulb of AdvL3 of Gnathostoma spp.
Species
Rows of cephalic bulb
I
G. spinigeruma
G. binucleatumb
G. turgidumc
G. binucleatumd
Gnathostoma sp.e
39–49
35–44
26–34
36–44
36–40
II
(44.3)
(38.7)
(30.8)
(40.2)
(38.0)
42–54
38–47
29–38
35–47
39–45
III
(47.3)
(42.4)
(34.0)
(43.5)
(42.3)
45–56
40–49
29–43
39–51
39–46
IV
(49.6)
(44.7)
(36.7)
(46.9)
(43.0)
a
Miyazaki (1954), based on the measurements of 26 larvae from fish (Channa argus; Ophiocephalus argus)
b
Almeyda-Artigas (1991), 30 larvae from fish (Petenia splendida)
c
Mosqueda-Cabrera et al. (2009), 11 larvae from frog (R. zweifeli)
d
Current study, 13 larvae from G. dormitor
e
Current study, 8 larvae from M. robustus
Consequently, the larvae isolated from the guavinos
correspond to G. binucleatum (Almeyda-Artigas 1991).
However, the comparison between the larvae from G.
dormitor and from M. robustus shows the excretory pore of
the latter, which is closer to the cephalic bulb (Table 1).
This suggests that these larvae might correspond to a
different species.
The larvae from M. robustus do not correspond to G.
turgidum, because the AdvL3 of this species are typically
encysted in the musculature of the frog, Rana zweifeli
(Mosqueda-Cabrera et al. 2009), have a lower number of
hooklets in the cephalic bulb (Table 2), and are smaller
1,530–2,007.4 (1,670.2). A new species of gnathostome
was recently described in Mexico, G. lamothei (BertoniRuiz et al. 2005); however, up to this date, the third stage of
the larvae of this species has not been characterized,
making the comparison impossible.
Based on the morphology of the cephalic bulb hooklets
of AdvL3, some authors have considered that such
larvae may constitute a new species of the genus Gnathostoma (Setasuban et al. 1991; Akahane et al. 1995).
Particularly in the case of AdvL3 of G. spinigerum
naturally and experimentally obtained, morphological variations or abnormalities in the cephalic bulb were recorded
(Rojekittikhun and Pubampen 1998; Rojekittikhun et al.
1998). These abnormalities were: presence of additional
rudimentary hooklets before the first row and after the
fourth one, as well as between the four rows of the cephalic
bulb; presence of a fifth row of hooklets; as well as
lobulated, branched, and fragmented hooklets. Taking into
account such observations, they concluded that the AdvL3
experimentally obtained, were very similar to the new type
of AdvL3 from eels of Nakhon Nayo, Thailand, described
by Setasuban et al. (1991), and to those reported by
Akahane et al. (1995). The AdvL3 collected from M.
45–58
43–52
33–42
44–54
48–52
IV-I
(52.0)
(48.2)
(39.6)
(49.9)
(49.8)
7.7
9.5
8.8
9.6
12.0
robustus in 1995 show morphological alterations similar to
those described by Rojekittikhun and Pubampen (1998),
and Rojekittikhun et al. (1998; Fig. 2a). However, the
AdvL3 isolated from M. robustus collected in 1998 show
different morphological alterations: the hooklets are not
disposed uniformly in rows and they do not have a clear
shape (they show fragmented scales of different shapes
and sizes, without the characteristic point of the hooklet;
Fig. 2b, c). Contrary to Rojekittikhun et al. (1998), who
obtained AdvL3 from naturally infected eels, we think that
the abnormalities observed in our research are not due to
interspecific variations but intraspecific. This fact is
supported by the results shown by Rojekittikhun and
Pubampen (1998), who recorded intraspecific variations
on AdvL3 of G. spinigerum experimentally obtained.
Therefore, the new type of larva reported by Akahane et
al. (1995) is the result of intraspecific variations on the
AdvL3 of G. spinigerum and not due to interspecific
morphological variations as indicated by these authors.
Furthermore, the intraspecific variability in Gnathostoma
has been documented on the basis of the shape of the
cephalic hooklets of AdvL3. In this sense, MartínezSalazar and León-Règagnon (2005) have recognized up
to six morphotypes of G. binucleatum. These authors
observed a minimum amount of variation among ITS2
sequences of three of their morphotypes. They conclude
that the variation among morphotypes 1, 2, and 3
is the result of intraspecific variability of the species
supported by morphology and DNA traits. Thus, the
abnormalities of cephalic bulb hooklets from AdvL3
cannot be considered as valid characteristics for differentiating species.
On the other hand, according to Möller (1987), there
is a close relationship between parasitic diseases and
pollution of aquatic environments; this relationship relies
Parasitol Res (2009) 105:1637–1642
on the vulnerability of the free-living larval stages of the
parasites and, therefore, the effect on the intermediate or
definitive hosts. Free-living infective stages of parasites
are directly exposed to toxins, and may be susceptible to
pollution (Poulin 1992; Overstreet 1997; MacKenzie
1999; Pietrock and Marcogliese 2003). However, little is
known about the direct effects of toxic agents on the freeliving stages of parasites, ectoparasites exposed to contaminants throughout their entire life, or the intermediate
hosts (Poulin 1992). In this sense, Šebelová et al. (2002)
have reported abnormalities in the attachment clamps of
diplozoon Paradiplozoon homoion, P. ergensi, P. megan,
and Diplozoon paradoxum (Monogenea: Diplozoidae)
isolated from gills of fish exposed to water pollution in
two river systems in Europe. The abnormalities observed
in the clamps included a reduction in the number and size
of clamps, asymmetry in their arrangement, and deformities. In this case, the authors concluded that pollutants
have a direct impact on diplozoon morphology.
Moreover, Rojekittikhun et al. (1998) state that abnormalities may be a consequence of a larger infection period
on the natural life cycle. However, in our opinion the
possible presence of toxins, or toxic agents in the pond
might be the cause of the alterations of the AdvL3 found in
M. robustus.
Taking into account that in our case, the pond has no
tributary source of water, and is located within an
agricultural and livestock breeding zone (activities which
involve an intensive use of plaguicides and other chemical
products), the host–parasite relationship may be exposed to
these pollutants. Such toxins may provoke the morphological alterations observed in the larvae. Initially, the toxic
exposure may affect the free-living phases (egg and secondstage larvae), and the effects may continue in the EaL3 and
AdvL3, during their development within the first intermediary host (Copepoda) and second intermediary host
(Pisces), respectively.
Finally, identifying the causes of the observed deformations of gnathostomes in M. robustus may provide
important environmental information. Once the causes are
identified, gnathostomes could be considered useful bioindicators of particular forms of environmental degradation
(Marcogliese 2005). Moreover, the reduced mobility of M.
robustus in the biotope makes it possible to identify the
precise source of pollution, as well as the time and duration
to the exposure.
Acknowledgements The authors are deeply grateful to Mr. Víctor
Rosales Pérez for his assistance in collecting the hosts; ScM Mario
Castañeda Sánchez for his aid in host dissection and examination; Dr.
Edmundo Sánchez Núñez for the critical review of this paper; and a
reviewer for providing helpful comments on the manuscript. The
seasonal permanence of the fishes in their habitat was not endangered
by the current research.
1641
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