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This article was downloaded by: [Cefas Lowestoft Laboratory], [Carlos Campos]On: 29 May 2012, At: 01:05Publisher: Taylor & FrancisInforma Ltd Registered in England and Wales Registered Number: 1072954 Registered office: MortimerHouse, 37-41 Mortimer Street, London W1T 3JH, UK
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Sponges as substrata and early life history of thetubulariid Zyzzyzus warreni (Cnidaria: Hydrozoa) inthe São Sebastião Channel, BrazilCarlos José Alexandre De Campos a , Alvaro Esteves Migotto b c , Ulisses Pinheiro d &Antonio Carlos Marques ca Centre for Environment, Fisheries & Aquaculture Science (Cefas), Weymouth, UKb Centro de Biologia Marinha, Universidade de São Paulo, São Sebastião, Brazilc Departamento de Zoologia, Instituto de Biociências, Universidade de São Paulo, SãoPaulo, Brazild Departamento de Zoologia, Centro de Ciências Biológicas, Universidade Federal dePernambuco, Recife, Brazil
Available online: 29 May 2012
To cite this article: Carlos José Alexandre De Campos, Alvaro Esteves Migotto, Ulisses Pinheiro & Antonio Carlos Marques(2012): Sponges as substrata and early life history of the tubulariid Zyzzyzus warreni (Cnidaria: Hydrozoa) in the SãoSebastião Channel, Brazil, Marine Biology Research, 8:7, 573-583
To link to this article: http://dx.doi.org/10.1080/17451000.2011.638641
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ORIGINAL ARTICLE
Sponges as substrata and early life history of the tubulariid Zyzzyzus
warreni (Cnidaria: Hydrozoa) in the Sao Sebastiao Channel, Brazil
CARLOS JOSE ALEXANDRE DE CAMPOS1*, ALVARO ESTEVES MIGOTTO2,3,
ULISSES PINHEIRO4 & ANTONIO CARLOS MARQUES3
1Centre for Environment, Fisheries & Aquaculture Science (Cefas), Weymouth, UK, 2Centro de Biologia Marinha,
Universidade de Sao Paulo, Sao Sebastiao, Brazil, 3Departamento de Zoologia, Instituto de Biociencias, Universidade de
Sao Paulo, Sao Paulo, Brazil, and 4Departamento de Zoologia, Centro de Ciencias Biologicas, Universidade Federal de
Pernambuco, Recife, Brazil
AbstractThe hydroid Zyzzyzus warreni is usually found in shallow coastal waters forming aggregations of solitary polyps embeddedin demosponges. Early life history transformations and settlement responses by the actinulae of this hydroid were studied inthe laboratory using 13 species of sponges and 2 species of algae collected in the Sao Sebastiao Channel (Brazil) assubstrata. The absence of oral tentacles and mouth in the actinulae and early events of metamorphosis suggest that theselarvae are unable to spend long periods in the plankton and attach quickly near conspecifics when a preferred substratum isencountered. The time required for settlement and the number of elicited settlings indicated four settlement responses: (a)frequent and short-time settlement, in actinulae exposed to Halichondria cebimarensis, Mycale angulosa, M. aff. americana,M. laxissima (skeleton) and Tedania ignis; (b) moderate and delayed settlement, in actinulae exposed to Aplysina caissara,A. fulva, Haliclona melana and M. microsigmatosa; (c) no settlement, in actinulae exposed to Suberites aurantiacus and to thealgae Hypnea musciformis and Sargassum cymosum; and (d) lethal response, in actinulae exposed to Amphimedon viridis,Aplysilla rosea, Dragmacidon reticulatum and M. laxissima. These responses indicate a considerable degree of speciesdiscrimination by the actinulae and are consistent with substrata used by the hydroid in the natural environment.
Key words: Porifera, Hydrozoa, Zyzzyzus warreni, settlement, life history, feeding behaviour
Introduction
Most hydroids have complex metagenetic life his-
tories which include the benthic polyp and the
pelagic medusa. In these animals, the metamorpho-
sis to the developed polyp involves a series of
morpho-physiological transformations, which may
occur by means of different strategies, including the
development of different larval forms (see Berking
1998; Muller & Leitz 2002). The life history of
tubulariid hydroids includes the development of a
lecithotrophic larva called actinula, which contains
tentacles formed inside the reproductive structure �the gonophore � just before release into the water
column (Berking 1998).
Aspects of the life history of tubulariids have been
described in the literature (e.g. Pyefinch & Downing
1949; Berrill 1952). However, very little is known
about the role of the actinulae on dispersal, selection
of substrata and demography of tubulariids.
Sponges are used as substrata by many species of
hydroids, which may thrive on or inside the sponges
(Puce et al. 2005). The potential benefits to both
groups of animals presumed to exist in this associa-
tion include trophic and reproductive aspects, such
as refuge from predators and protection against
water movement (Bacescu 1971; Klitgaard 1995;
Duarte & Nalesso 1996; Ribeiro et al. 2003). For
instance, anthoathecate tubulariids (e.g. species of
*Correspondence: Carlos Jose Alexandre de Campos, Centre for Environment, Fisheries & Aquaculture Science (Cefas), Weymouth
Laboratory, Barrack Road, The Nothe, Weymouth, Dorset DT4 8UB, UK. E-mail: [email protected]
Published in collaboration with the University of Bergen and the Institute of Marine Research, Norway, and the Marine Biological Laboratory,
University of Copenhagen, Denmark
Marine Biology Research, 2012; 8: 573�583
(Accepted 4 October 2011; Published online 25 May 2012)
ISSN 1745-1000 print/ISSN 1745-1019 online # 2012 Taylor & Francis
http://dx.doi.org/10.1080/17451000.2011.638641
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Hybocodon and Zyzzyzus) are commonly found on
demosponges (see Warren 1906; Hirohito 1988;
Petersen 1990).
Zyzzyzus warreni Calder, 1988 has been observed
in sheltered shallow coastal waters in Bermuda
(Calder 1993), on rocky shores in southeastern
Brazil (Migotto & Silveira 1987; Migotto 1996)
and French Lesser Antilles (Galea 2008), mangrove
roots in northeastern Brazil (Calder & Mayal 1998)
and Belize (Calder 1991), bays in South Africa and
Mozambique (Millard 1975) and the Netherlands
Antilles (de Kruijf 1977), and in protected areas in
Japan (Hirohito 1988), Puerto Rico (Wedler &
Larson 1986) and Colombia (Bandel & Wedler
1987), forming aggregations of polyps on a number
of different species of sponges (Warren 1906; Mi-
gotto & Silveira, 1987; Calder 1988).
The objective of this study was to investigate the
degree of substrate selection by the actinulae of
Z. warreni and describe the early life history of this
hydroid. This investigation was undertaken with the
eventual intention of providing new evidence to-
wards clarification of the taxonomic position of this
species, which has been much debated (Petersen
1979, 1990; Marques & Migotto 2001; Campos
et al. 2007).
Materials and methods
Life history studies and settlement experiments were
undertaken between February and April 2002, when
many polyps of Zyzzyzus warreni were releasing
actinulae. Actinulae and polyps were reared in Petri
dishes containing filtered sea water (FSW) and fed
with Artemia nauplii. Polyps were measured under a
Zeiss Axiophot microscope equipped with Zeiss KS
300, after being anaesthetized in a 1:1 solution of
7.5% MgCl2 and seawater and preserved in 4%
formaldehyde. The cnidome (nematocyst composi-
tion and measurements) was studied in actinulae
and juvenile polyps (3, 12 and 18 h old). Only
capsules of undischarged nematocysts were mea-
sured. The nematocyst nomenclature adopted is that
of Mariscal (1974) and Millard (1975).
Samples of sponges, polyps and algae were
hand-picked from three sites in the Sao Sebastiao
Channel (southeast Brazil). The sponges Mycale
angulosa (Duchassaing & Michelotti, 1864), Mycale
microsigmatosa Arndt, 1927, and Tedania ignis
(Duchassaing & Michelotti, 1864) containing polyps
were sampled from an iron frame deployed at depth
of 3 m in the shallow bay of Praia do Segredo
(23849?42??S; 45825?16??W). In addition, 10 other
species of sponges were collected from an adjacent
rocky shore at Ponta do Jaroba (23849?68??S;
45825?28??W): Amphimedon viridis Duchassaing &
Michelotti, 1864, Aplysina caissara Pinheiro &
Hajdu, 2001, Aplysina fulva Pallas, 1766, Aplysilla
rosea (Barrois, 1876), Dragmacidon reticulatum
(Ridley & Dendy, 1886), Haliclona melana (Muricy
& Ribeiro, 1999), Mycale aff. americana (Van Soest,
1984), Mycale laxissima (Duchassaing & Michelotti,
1864), Halichondria cebimarensis Carvalho & Hajdu,
2001, and Suberites aurantiacus (Duchassaing &
Michelotti, 1864) (Custodio & Hajdu 2011). The
red alga Hypnea musciformis (Wulfen) J. V. Lamour-
oux and the brown alga Sargassum cymosum C.
Agardh were sampled from an adjacent sandy beach,
Praia de Guarapocaia (Ilhabela) (23844?80??S;
45820?94??W). Samples were transported to the
laboratory in plastic containers (1500 ml) containing
seawater. In the laboratory, samples were transferred
to large plastic trays receiving continuous trickle flow
of FSW. Actinulae released from adult polyps were
collected from the water column on a daily basis
using a pipette and maintained in glass bowls
containing FSW (salinity�34 psu) kept under
constant room temperature (258C) with a 12 h
light/12 h dark photoperiod.
Settlement experiments were performed in 24-well
Cell Culture Clusters (Corning). Each well contain-
ing 3 ml of FSW received:0.25 cm3 of sponge or
algae as substrata and one actinula. Two sets of
experiments were conducted. In the first, all species
of sponges and algae were used. Each experiment
consisted of 15 actinulae per substratum and a
further 15 actinulae without substratum as control.
Actinulae exposed to M. laxissima died immediately
(see Results), probably due to the deleterious effect
of mucus released from the sponge (see Hajdu &
Rutzler 1998). To confirm this, fragments of
M. laxissima were rinsed with FSW and the clean
skeleton of the sponge was used in a further
experiment.
Six species of sponges (A. fulva, A. viridis,
H. melana, M. aff. americana, M. angulosa and
T. ignis) were selected for a second experiment.
This consisted of 45 actinulae per substratum and
15 actinulae without substratum as control. The
number of settled actinulae was recorded every 20
min during the first experiment (total duration�17
h) and every 10 min during the second experiment
(total duration�08:20 h). Seawater in culture cells
was replaced hourly. The emergence of a protrusion
in the aboral pole of the actinulae was the criterion
for considering a successful settlement. This juve-
nile-specific structure has been described in
Acharadria spp. (see Pyefinch & Downing 1949;
Berrill 1952).
The differences in the number of settled actinulae
between substrata in the second experiment were
analysed by one-way ANOVA, followed by Tukey’s
574 C. J. A. de Campos et al.
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family error test (a�0.05) for post-hoc comparisons
of means. Confidence intervals were determined for
pairwise differences between means. The first ana-
lysis was performed for the total number of settled
actinulae during the experiment and the second
analysis for the total number of settled actinulae at
60 min of settlement.
Representatives of sampled sponges were sub-
mitted to the Porifera collection of the Museu
Nacional, Universidade Federal do Rio de Janeiro
(MNRJ), Rio de Janeiro: MNRJ 6749 and 6758: A.
fulva; MNRJ 6750: M. microsigmatosa; MNRJ 6752
and 6753: H. melana; MNRJ 6754: S. aurantiacus;
MNRJ 6756: D. reticulatum; MNRJ 6757: A. rosea;
MNRJ 6759: A. viridis; MNRJ 6760: A. caissara;
MNRJ 6761: T. ignis. Representatives of collected
polyps were submitted to the Cnidaria collection of
the Museu de Zoologia da Universidade de Sao
Paulo: MZUSP 1983.
Results
Morphology and behaviour of actinulae
The morphology of polyps of Zyzzyzus warreni was
described previously (Campos et al. 2007). Fully
developed female gonophores contained between
one and four actinulae (Figure 1a). Actinulae were
released from the gonophore in a series of 2�19
Figure 1. Life history stages of Zyzzyzus warreni. Actinulae (a, b, c); newly metamorphosed polyps with 2 h (d), 10 h (e), and 30 h (f) on
the sponge Mycale angulosa; adult polyp with two developing male gonophores (g); female gonophore with developing actinulae (h). Scale
bars �250 mm.
Selection of substrata by Zyzzyus warreni 575
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(n�25) pulsations per minute and per event.
A small population of 25 adult polyps released 70
actinulae during a single night. Just before release
into the water column, actinulae projected their
aboral poles towards the circular apical orifice of
the gonophore.
At this stage, each actinula consisted of a cone-
shaped body 316�474 mm long and 330�587 mm
wide at the aboral pole, with one whorl of 6�16
aboral, concentrically disposed filiform tentacles,
764�1432 mm long and 27�97 mm wide at their
bases (Figure 1b,c). Tentacles were flattened basally
and rounded distally in cross-section. The distance
between adjacent tentacular bases was equivalent to
the diameter of tentacles (Figure 1B). Clusters of
four different types of nematocysts (small stenoteles,
heterotrichous microbasic euryteles, homotrichous
microbasic euryteles and desmonemes) were ob-
served along the tentacles and on the terminal
swollen tip. None of the:104 actinulae had devel-
oped a mouth at this stage.
Actinulae did not show active swimming ability
inside culture cells. However, their tentacles exhib-
ited slow movements around the edges of these
compartments with no permanent attachment ob-
served in any of the experiments (see below). Once
in contact with the preferred biogenic substrata,
most tentacles became orientated towards the sub-
stratum. This behaviour was not observed in acti-
nulae exposed to lethal sponges (see below).
Actinulae remained viable for at least 3 days if not
in contact with biogenic substrata.
Settlement
Actinulae of Zyzzyzus warreni exhibited different
settlement responses according to the species used
as substrata. No settlement or death of actinulae was
recorded in any of the controls.
There were no settlements on the algae Hypnea
musciformis and Sargassum cymosum. In the first
experiment, 8 of the 13 species of sponges elicited
settlement. There were no settlements on the sponge
Suberites aurantiacus, and the actinulae died in
contact with four species of sponges. Of these,
Dragmacidon reticulatum and Amphimedon viridis
were the most lethal, i.e. 100% of actinulae died
during the first 20 min of exposure. All actinulae
died within 2 h in the experiments with Aplysilla rosea
and Mycale laxissima. In all cases of contact with
lethal sponges, body maceration and tentacle resorp-
tion were observed during the first minutes of
exposure, leading to death of actinulae. The highest
rates of settlement were observed in Halichondria
cebimarensis (100% of actinulae settled within 40 min
in the first experiment).
In the second experiment, the time required for
settlement and metamorphosis ranged between 10
min (in actinulae exposed to Mycale angulosa and
Tedania ignis) and 6 h (with the exception of a single
outlier settlement at:17 h on Aplysina caissara).
Actinulae used in controls remained alive in all
experiments and during the whole duration of the
experiment (17 h).
The sponges Mycale aff. americana, M. laxissima
(skeleton), and T. ignis elicited settlement and
metamorphosis in more than 50% of the actinulae
within the first 60 min (Figure 2). High settlement
rates were observed in each of these sponges over the
following 4 h, on which 100% (M. aff. americana),
93% (M. laxissima) and 80% (T. ignis) of the
actinulae settled.
The sponges Aplysina caissara, A. fulva, Haliclona
melana, M. angulosa and M. microsigmatosa elicited a
lower number of successful settlements than those
observed in the first group of sponges (Figure 2).
None of these sponges elicited more than 30% of
successful settlements during the first hour of the
experiment. The ratio of settled actinulae
was �50% in the tests with A. caissara, A. fulva
and M. microsigmatosa (maximum after 4 h). Settle-
ment was B50% in the tests with H. melana (max-
imum of 13% at 2:40 h) and M. angulosa (maximum
of 47% at 3 h) (Figure 2).
The second experiment corroborated the inter-
species differences in settlement rates observed
during the first experiment, with the exception of
M. angulosa (Figure 3), on which settlement was
quicker (from 47% actinulae settled at 3 h to 98%
actinulae settled within the first hour). ANOVA
revealed statistically significant (F�93.28;
p�0.000) differences between the total number of
actinulae settled. The Tukey’s test suggested the
following three groups of sponges for 99% con-
fidence intervals: M. aff. americana, T. ignis and
M. angulosa; A. fulva; H. melana and A. viridis.
When considering 60 min as the reference settle-
ment time, T. ignis elicited a higher number of
successful settlements in the second experiment
(from 67 to 84%), whereas M. aff. americana
elicited a lower number of successful settlements
in the second experiment (from 60 to 40%). T. ignis
elicited higher numbers of successful settlements in
the second experiment (from 80 to 91%), whereas
M. aff. americana elicited lower numbers (from 100
to 96%) (Figure 3). Aplysina fulva elicited later
successful settlements than the remaining sponges
of the group (except H. melana): between 70 and 80
min during the first experiment (Figure 2), and
from about 5 h (53%) to 8 h (40%) during the
second experiment (Figure 3). Similar results were
obtained in the two experiments with Haliclona
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melana, which elicited settlements after:3 h and
13% of actinulae settled in the first experiment
(Figure 2) and 7% in the second experiment
(Figure 3). Amphimedon viridis confirmed high
lethal activity (100% of the actinulae died within
10 min of exposure).
Figure 2. Cumulative percentage of actinulae of Zyzzyzus warreni settled on sponges during the first experiment.
Selection of substrata by Zyzzyus warreni 577
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Based on these observations, four settlement re-
sponses were recognized: (a) high and short-time
larval settlement, in actinulae exposed to H.
cebimarensis, M. angulosa, M. aff. americana, M.
laxissima and T. ignis; (b) moderate and delayed larval
settlement, in actinulae exposed to A. caissara,
A. fulva, H. melana and M. microsigmatosa; (c) no
settlement, in actinulae exposed to the algae
H. musciformis and S. cymosum, and to the sponge S.
aurantiacus; and (d) lethal response, in actinulae
exposed to A. rosea, A. viridis and D. reticulatum.
Metamorphosis
During the first minutes of permanent attachment to
preferred substrata, the tentacle tips of the actinulae
adhered temporarily to the surface of the sponges
(Figure 1d). After this adhesion, the aboral protru-
sion emerged from the actinular body, enlarged
proximally presumably via endodermic thickening
and penetrated the sponge tissue. From this enlarged
portion, the hydrocaulus extended and differentiated
upwards, whereas the hydrorhiza extended down-
wards (Figure 1e,f). Three-hour polyps had two
Figure 3. Cumulative percentage of actinulae of Zyzzyzus warreni settled on sponges during the second experiment.
578 C. J. A. de Campos et al.
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classes of stenoteles, two classes of euryteles, and
desmonemes.
During the first 20 h of settlement, the hydro-
caulus increased from 307�356 mm long at 3 h to
1007�1680 mm long at 12 h (Figure 4). An inverse
trend was observed in the hydranth, which de-
creased in length from 479�610 mm at 3 h to 248�337 mm at 12 h. During this period, the aboral
tentacles decreased from 46�89 mm wide at 1 h to
35�55 mm wide at 20 h. Oral tentacles became
externally visible in the hypostome region of the
hydranth:10 h after the beginning of metamor-
phosis (Figure 1f), initially as four small dermic
evaginations that continued to grow out, reaching
98�157 mm long and 29�53 mm wide in 20 h.
Within 20 h, the aboral tentacles reached 246�646
mm long. Most of the differentiation occurred
during this time, the hydranth becoming gradually
vasiform near the base and narrowed in the region
of the hypostome. At:27 h after the beginning of
metamorphosis, the whorl of slightly capitate oral
tentacles and the whorl of filiform aboral tentacles
were observed; meanwhile, endodermal canals were
visible in the hydrocaulus. At:30 h after the
beginning of metamorphosis, the mouth opened
and the polyp was able to search for prey
(Figure 1g). The aboral tentacles were resorbed,
underwent restructuring and lost terminal knobs.
Newly settled polyps occasionally developed new
aboral tentacles.
When sponges were removed from Petri dishes,
primary polyps continued development of a tubular,
thin-walled hydrorhiza covered by filmy perisarc,
often longer than the hydrocaulus itself. Hydrorhi-
zal structures developed until 36 h after metamor-
phosis.
In the laboratory, polyps did not survive until the
development of reproductive structures.
Feeding behaviour
Two-day-old polyps had the ability to search actively
for prey. Fragments of nauplii were caught by aboral
tentacles and taken into the mouth through the oral
tentacles. Foraging for prey consisted of two main
behavioural patterns: (1) a passive pattern, charac-
terized by non-moving, upright posture of the polyp
and slow upward/downward movements of aboral
tentacles, by means of which prey and particles were
trapped, retained or intercepted; and (2) an active,
most predominant pattern, characterized by twisting
and bending of the polyp in different directions, by
means of which prey were transported to the feeding
area, caught by aboral tentacles and delivered to the
mouth. In both patterns, aboral tentacles joined with
oral tentacles to form a ‘bridge’ by which prey was
conducted into the mouth. Actinulae were never
observed to use oral tentacles to capture prey.
Swallowing of an Artemia nauplius by adult polyps
(Figure 1h) took approximately:1 min.
Discussion
Most studies on life history of species of Acharadria
and Tubularia have mentioned the existence of one
whorl of oral tentacles (e.g. Pyefinch & Downing
1949; Hawes 1955; Nagao 1960, 1965; Widersten
1968; Yamashita et al. 1997) and a mouth (Zamponi
& Correa 1988) in newly liberated actinulae. The
actinulae of Zyzzyzus warreni do not contain any of
these structures at this stage. They are developed at a
later stage when successful settlement near conspe-
cifics is achieved. In addition, the actinulae of
Z. warreni are larger than those of other tubulariids
(cf. Zamponi & Correa 1988; Yamashita et al. 2003).
We regard these traits as pre-requisites for a short
planktonic life span and maintenance of larval
competence during metamorphosis. This condition,
Figure 4. Morphometrics of Zyzzyzus warreni settled on the sponge Mycale angulosa during the first 20 h of metamorphosis (n�30).
Selection of substrata by Zyzzyus warreni 579
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named as metamorphic competence by Hadfield
et al. (2001), is characteristic of many marine
invertebrate larvae (e.g. cnidarian planulae, mollus-
can veligers, barnacle cyprids).
The morphological changes that take place during
settlement and early metamorphosis have been
described in some detail for some tubulariid species
(Pyefinch & Downing 1949; Berrill 1952). These are
physiologically mediated by changes in nematocyst
composition and dynamics (Kawaii et al. 1997;
Yamashita et al. 2003). In Z. warreni, these processes
involve the development of juvenile structures (mor-
phological changes in the hydranth, elongation of the
hydrocaulus and, at a later stage, development of
oral tentacles) and increase in size of stenoteles.
These changes represent adaptations of this species
to enhance settlement in the preferred substrata
during the period of larval competence.
The means of attachment to substrata are a
character traditionally used for genera distinction
in the Tubulariidae (see Petersen 1979, 1990;
Marques & Migotto 2001). The morphological
diversity of hydrorhizal processes in polyps of Z.
warreni described by Campos et al. (2007) and the
development of a tubular hydrorhiza observed in this
study demonstrate that this phenotype is determined
by the substratum-derived factors discussed above.
Tubulariids have developed a variety of associa-
tions with animals and plants, namely gorgonians
(Silveira & Migotto 1984; Puce et al. 2008), poly-
chaetes (Tardent 1980), barnacles and mussels
(Migotto & Marques 1999) and seagrasses (Nagao
1960). Acharadria japonica, Hybocodon prolifer and
species of Zyzzyzus have been found almost exclu-
sively on sponges (see Hirohito 1988; Petersen
1990). However, many of these associations are not
obligatory. For instance, A. larynx may settle on
species of Enteromorpha, Ectocarpus and Laminaria,
this preference often dependent on the local density
of these substrata (Pyefinch & Downing 1949).
Under artificial conditions, however, A. crocea and
A. larynx are able to settle on surfaces free from
biogenic substrata after delayed settlement (see
Pyefinch & Downing 1949; Kawaii et al. 1997;
Yamashita et al. 1997). In contrast, Z. warreni occurs
only on demosponges in Brazil and other areas, e.g.
in Bermuda on Tedania ignis (Calder 1988); in the
Santa Marta coast of Colombia, on Tedania sp.
(Bandel & Wedler 1987); in Sagami Bay Japan, on
Ceraochalina differentiata, Callyspongia fibrosa,
Haliclona clathrata, H. permollis and Clathria
fasciculata (Hirohito 1988). In our studies, none of
the actinulae of Z. warreni settled on algae or on
surfaces free of biogenic substrata. Most sponges
elicited either settlement or death of the actinulae. In
experiments with the sponge Suberites aurantiacus
and the algae Sargassum cymosum and Hypnea
musciformis there were neither settlement nor death
of the actinulae. Although S. cymosum is often found
in association with the sponges Mycale angulosa
(Duarte & Nalesso 1996) and M. laxissima (pers.
obs.), Z. warreni is never found on the algae.
There are approximately 120 species of demos-
ponges recorded in the Sao Sebastiao Channel
(Hajdu et al. 2002). The sponges used in this study
belong to the group of the 25 most frequently found
sponges in the channel (see Santos & Hajdu 2001).
Of these, Mycale angulosa, M. laxissima, M.
microsigmatosa and Tedania ignis are preferred sub-
strata used by the hydroid in the natural environ-
ment. These soft sponges constitute a significant
proportion of the biomass available for actinular
settlement and vary considerably with respect to
their encrusting and massive habits (see Lavrado
2006), which facilitates tissue penetration by newly
settled polyps. The lack of association between
Z. warreni and Halichondria cebimarensis, Aplysina
caissara, A. fulva and M. aff. americana could be
explained by the combined effect of abiotic and
biotic factors. For instance, H. cebimarensis is a rare
species in the Sao Sebastiao Channel; the typical
areas of occurrence of A. caissara are highly energetic
rocky coasts (Pinheiro & Hajdu 2001); A. fulva is
occasionally associated with the zoanthid Palythoa
caribaeorum (Pinheiro & Hajdu 2001) and M. aff.
americana is often found underneath rocks. These
constitute unfavourable conditions for settlement of
Z. warreni. In contrast, the diverse and abundant
fauna of crustaceans, polychaetes, molluscs and
hydroids known to live in association with
M. angulosa and M. microsigmatosa (Duarte &
Nalesso 1996; Ribeiro et al. 2003) do not prevent
colonization of Z. warreni on these sponges. In fact,
ophiuroids and polychaetes associated with M. aff.
americana were observed to prey upon actinulae of
Z. warreni during laboratory experiments. The
association of H. cebimarensis with ophiuroids, tube-
worms, ectoprocts, Sargassum and calcareous algae
(Carvalho & Hajdu 2001) could affect the successful
settlement of Z. warreni.
It was outside the scope of this study to evaluate
the role of physical or chemical stimuli during
settlement and metamorphosis of Z. warreni on
biogenic substrata. We hypothesize, however, that
chemical signalling from sponges plays a significant
role in determining the distribution of this hydroid.
From an evolutionary point of view, Puce et al.
(2005, p. 78) noted that associations between
hydroids and sponges ‘evolved as a form of parasit-
ism, in which some hydroid species succeeded in
overcoming the chemical defences that prevented the
settlement of other organisms on most sponges’.
580 C. J. A. de Campos et al.
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The death of actinulae of Z. warreni exposed to
Amphimedon viridis, Aplysilla rosea and Dragmacidon
reticulatum could be associated with allelopathic
defensive mechanisms exhibited by these species
(see Berlinck et al. 1996; Muricy & Silva 1999).
Furthermore, sponges kept in laboratory conditions
often disintegrate rapidly. It is likely that some of the
toxic reactions observed were due to decaying
sponge tissues resulting from the in-vitro conditions.
High cytotoxic, antifungicidal, antiviral and antibac-
terial activities have been identified in the halitoxin
and amphitoxin complex isolated from A. viridis
from Brazil (Berlinck et al. 1996). Cytotoxic activity
has been also identified in extracts of A. rosea
(Berlinck et al. 2004) and A. fulva (Aiub et al.
2006). Similarly, Nunez et al. (2008) found
dibromotyrosine-derived compounds in A. fulva.
Biotoxic activity has not been found in D.
reticulatum, M. aff. americana and Haliclona melana
from Brazil (e.g. Sole-Cava et al. 1981; Muricy et al.
1993; Rangel et al. 2001). Dresch et al. (2005)
tested 20 species of sponges for the presence of
lectinic and haemolytic activity and did not find any
of these activities in Tedania ignis collected from
Santa Catarina State. However, high cytotoxic
activity has been detected in this species from
Florida Keys (Schmitz et al. 1983). It should be
noted that allelopathic defensive mechanisms may
vary significantly with the geographical location of
individual populations. As noted by Nunez et al.
(2008), the composition of secondary metabolites in
sponges can be influenced by multiple factors, such
as habitat, exposure to predation, association with or
infection by microorganisms, individual biosynthesis
or even laboratory techniques used for the purposes
of extraction and purification of compounds.
In summary, our study shows that polyps of Z.
warreni are not able to maintain an independent
existence from sponges. The establishment of the
hydroid�sponge pairing results from considerable
species discrimination by the actinulae during their
competent stage. Further studies are required to
understand the role of chemical signalling on this
selective advantage.
Acknowledgements
We thank Marcio Custodio (IB � USP) for his
constructive comments during this investigation,
and to Stefania Puce and an anonymous referee for
reviewing and improving an early version of the
manuscript. A. E. Migotto and A. C. Marques
received financial support from the Conselho Na-
cional de Desenvolvimento Cientıfico e Tecnologico
(CNPq; 305608/2006-1, 481309/2007-1, 302596/
2003-8, 304720/2009-7, and 562143/2010-6) and
FAPESP (1998/07090-3, 2001/02626-7, 2003/
02432-3, 2004/09961-4, 2006/05821-9, and 2011/
50242-5). U. Pinheiro received financial support
from Fundacao de Amparo a Ciencia e Tecnologia
do Estado de Pernambuco.
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