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<strong>Porifera</strong> research: Biodiversity, innovation <strong>and</strong> sustainaBility - 2007<br />

<strong>Symbiotic</strong> <strong>relationships</strong> <strong>between</strong> <strong>sponges</strong> <strong>and</strong> <strong>other</strong><br />

organisms from the Sea of Cortes (Mexican Pacific<br />

coast): same problems, same solutions<br />

Enrique Ávila (1,2*) , José Luís Carballo (1) , José Antonio Cruz-Barraza (1,2)<br />

(1) Laboratorio de Ecología del Bentos, Instituto de Ciencias del Mar y Limnología. Universidad Nacional Autónoma de<br />

México, Estación Mazatlán, Avenida Joel Montes Camarena S/N, Apartado Postal 811, Mazatlán 82000, México. Tel.<br />

+52 669 985 28 45. Fax: +52 669 982 61 33. kike@ola.icmyl.unam.mx<br />

(2) Posgrado en Ciencias del Mar y Limnología, UNAM, Mazatlán, México<br />

Abstract: This study provides a morphological description of three symbiotic associations <strong>between</strong> <strong>sponges</strong> (Haplosclerida)<br />

<strong>and</strong> <strong>other</strong> macroorganisms from the Sea of Cortes (Mexican Pacific Ocean). These associations include: (1) a two-sponge<br />

association (Haliclona sonorensis/Geodia media), (2) a sponge-red macroalga association (Haliclona caerulea/Jania adherens)<br />

<strong>and</strong> (3), a sponge-coral association (Chalinula nematifera/Pocillopora spp.). So far these interactions seem to be obligatory<br />

for the <strong>sponges</strong> (Haliclona spp. <strong>and</strong> C. nematifera), since we have never found them living in isolation. Interestingly, similar<br />

associations have been described from <strong>other</strong> places around the world. Associations quite similar to (1) have been described<br />

from the Caribbean, <strong>and</strong> associations (2) <strong>and</strong> (3) are comparable to <strong>other</strong>s described from the Western Pacific. Instead of<br />

comparing these associations with their “sibling” associations worldwide, we discussed the ability of haplosclerid <strong>sponges</strong><br />

to form symbiotic associations with <strong>other</strong> organisms, since these <strong>sponges</strong> pertain to the group of which the most associations<br />

have been described.<br />

Keywords: Sea of Cortes, sponge-alga, sponge-coral, symbiotic associations, two-sponge<br />

Introduction<br />

Sponges are one of the major phyla found in the hardsubstrate<br />

marine benthos (Sarà <strong>and</strong> Vacelet 1973). One of their<br />

more interesting characteristics is that they are able to establish<br />

a great diversity of <strong>relationships</strong> (mutualism, commensalism<br />

<strong>and</strong> parasitism) with unicellular <strong>and</strong> multicellular organisms<br />

(Palumbi 1985, Rützler 1990, Magnino <strong>and</strong> Gaino 1998, Ilan<br />

et al. 1999, Wulff 1999, Thakur <strong>and</strong> Müller 2004).<br />

Most of these <strong>relationships</strong> have been reported in the<br />

Caribbean (West 1979, Rützler 1990, Wulff 1997a, 1997b,<br />

1999, Wilcox et al. 2002), Mediterranean Sea (Uriz et al.<br />

1992, Gaino <strong>and</strong> Sará 1994), Red Sea (Meroz <strong>and</strong> Ilan 1995,<br />

Ilan et al. 1999), Indo-Pacific region (Steindler et al. 2002,<br />

Calcinai et al. 2004) <strong>and</strong> Western Pacific (Vacelet 1981,<br />

Trautman et al. 2000). Surprisingly, in a large number of<br />

cases, the same species are involved in similar interactions in<br />

different oceans (Ilan et al. 1999, Wulff 2006). For example,<br />

the <strong>sponges</strong> Haliclona caerulea Hechtel, 1965, Haliclona<br />

cymaeformis Esper, 1794 <strong>and</strong> Dysidea janiae (Duchassaing<br />

<strong>and</strong> Michelotti, 1864) are species found to establish similar<br />

interactions with red macroalgae (Vacelet 1981, Rützler 1990,<br />

Trautman et al. 2000, Carballo <strong>and</strong> Ávila 2004). However, it is<br />

unknown whether this group of “cosmopolitan” associations<br />

occurs in the East Pacific Ocean.<br />

147<br />

The order Haplosclerida (Demospongiae) is the group<br />

in which the most of the symbiotic <strong>relationships</strong> have been<br />

registered with the family Chalinidae Gray, 1867 accounting<br />

for more than 50% of the associations described in this<br />

order (see discussion). Sponges of this order can establish<br />

associations with microorganisms such as bacteria (Vacelet et<br />

al. 2001), cyanobacteria (Steindler et al. 2002), dinoflagellates<br />

(Garson et al. 1998) <strong>and</strong> zoochlorellae (Frost <strong>and</strong> Williamson<br />

1980), <strong>and</strong> with macroorganisms such as polychaetes (Dauer<br />

1974), macroalgae (Vacelet 1981), mangroves (Ellison et al.<br />

1996), barnacles (Ilan et al. 1999), hydrozoans (Schuchert<br />

2003), anthozoans (West 1979), ophiurids (Henkel <strong>and</strong><br />

Pawlik 2005), insects (Gaino et al. 2004) <strong>and</strong> <strong>other</strong> <strong>sponges</strong><br />

(Wilcox et al. 2002).<br />

In the present study, we describe three interactions involving<br />

haplosclerid <strong>sponges</strong> from the Sea of Cortes (Mexican Pacific<br />

Ocean). They are a two-sponge association (Haliclona<br />

sonorensis-Geodia media), a sponge-alga association<br />

(Haliclona caerulea-Jania adherens) <strong>and</strong> a sponge-coral<br />

association (Chalinula nematifera-Pocillopora spp.). We<br />

discuss the surprising parallelism that exists worldwide,<br />

given that very similar interactions occur in different oceans.<br />

In addition, we comment on the characteristics that this group<br />

– in which more symbiotic <strong>relationships</strong> have been registered –<br />

has in order to establish these symbiotic associations.


148<br />

Material <strong>and</strong> methods<br />

Specimens of the three associations were collected by<br />

SCUBA diving from 2 to 12 m depth, in four localities from<br />

the Sea of Cortes (Eastern Pacific Ocean, Mexico) (Fig. 1).<br />

We followed the techniques described by Rützler (1974) for<br />

spicule <strong>and</strong> tissue preparations for light microscopy. Crosssections<br />

of the specimens were washed in distilled water<br />

<strong>and</strong> then dried on a cover glass <strong>and</strong> coated with gold for<br />

scanning electron microscope (SEM) observations. A number<br />

of 20 to 50 spicules chosen r<strong>and</strong>omly were measured (length<br />

x width) from each of the specimens studied. The number<br />

<strong>between</strong> brackets in each description is the average. After<br />

the description, the specimens were fixed in formaldehyde<br />

4% <strong>and</strong> after 24 h they were transferred to 70% alcohol for<br />

their preservation. All the specimens were deposited in the<br />

Colección de Esponjas of the Instituto de Ciencias del Mar<br />

y Limnología, UNAM (LEB-ICML-UNAM), in Mazatlán<br />

(Mexico).<br />

In the Haliclona sonorensis/Geodia media association, the<br />

surface of G. media covered by H. sonorensis was estimated.<br />

First we took photographs of the specimens, then we<br />

determined the covered area (%) using the computer program<br />

Coral Point Count with Excel extensions (CPCe) (Kohler <strong>and</strong><br />

Gill 2006). The frequency of the C. nematifera/Pocillopora<br />

spp. association was determined in three transects of 50 m<br />

length at a depth <strong>between</strong> 4 to 6 m. In each one of these<br />

transects we chose 20 colonies of coral at r<strong>and</strong>om, <strong>and</strong><br />

determined the percentage of these containing sponge. In<br />

the same area, we also checked if the sponge was on an<strong>other</strong><br />

type of substratum. For each sample of the association we<br />

determined the species of coral <strong>and</strong> estimated the percentage<br />

of the colony overgrown by the sponge as number of branches<br />

with sponge of the total of branches.<br />

Results<br />

Association Haliclona sonorensis Cruz-Barraza <strong>and</strong><br />

Carballo, 2006 – Geodia media Bowerbank, 1873<br />

Material examined. Eleven specimens of the association<br />

were collected <strong>between</strong> 2 <strong>and</strong> 5 m depth in two localities<br />

from the northern Sea of Cortes: Punta Cazón (Bahía Kino,<br />

Sonora, 28°52’20” N, 112°02’01” W), <strong>and</strong> Punta Pinta (La<br />

Choya, Puerto Peñasco, Sonora, 31°18’05” N, 113°59’11”<br />

W) (Fig. 1), from August 2000 to April 2005.<br />

Description of the species involved in the association. The<br />

epizoic sponge was identified as Haliclona sonorensis Cruz-<br />

Barraza <strong>and</strong> Carballo, 2006, which is a cushion-shaped sponge<br />

from 2 to 5 mm in thickness (Fig. 2A). Consistency is soft,<br />

compressible, but fragile <strong>and</strong> brittle. The surface is smooth<br />

<strong>and</strong> the ectosomic layer is not easily detachable. The color is<br />

pinkish violet in life <strong>and</strong> ocre or light brown in alcohol. The<br />

oscules are scarce, <strong>and</strong> circular or oval-shaped (from 0.5 to 1<br />

mm in diameter), situated at the summits of volcano-shaped<br />

elevations. The skeletal material is constituted by oxeas that<br />

measure: 77-(112)-150 x 2-(5.6)-10 µm.<br />

The supporting sponge was identified as Geodia media<br />

Bowerbank, 1873. This is a massive-incrusting to massive<br />

amorphous sponge (from 3.5 to 8 cm thick). The surface is<br />

irregular, smooth to the naked eye, but finely rough to the<br />

touch. The natural color of the surface is from dark-brown to<br />

white. The choanosome is yellowish or beige. Small ostialpores<br />

from 150 to 300 µm are regularly distributed on the<br />

surface. The oscules are contained in several small, circular<br />

or oval-shaped well-defined flattened sieves (containing<br />

from 7 to more than 100 oscules). The oscules measure from<br />

0.22 to 2.5 mm in diameter. Consistency of the ectosome is<br />

very hard due to the cortex of sterrasters. The choanosome<br />

is cavernous <strong>and</strong> very densely spiculated, with a firm <strong>and</strong><br />

slightly compressible consistency. The skeletal material is<br />

constituted by megascleres: oxeas, 620-(1430)-1950 x 10-<br />

(31)-42 µm; large styles, 620-(1077)-1260 x 22-(36)-45<br />

µm; strongyloxeas, 150-(197.2)-292 x 2.5-(4.9)-7.5 µm;<br />

plagiotriaenes, 550-(1078)-1700 µm rabdome length; <strong>and</strong><br />

anatriaenes, 1120-(1410)-2040 µm rabdome length, <strong>and</strong><br />

microscleres: sterrasters, 25-(62.8)-90 µm oxyasters, 20-<br />

(27.2)-45 µm; oxyspherasters, 6.3-(9.5)-13 µm.<br />

Description of the association. The specimens of the<br />

association were found attached to the rocky substrata,<br />

covering areas from 8 x 6.5 to 20 x 15 cm, approximately.<br />

H. sonorensis forms a thin layer that covers up to 57 % of<br />

the surface of G. media, while the surface that is not covered<br />

by the sponge is occupied by <strong>other</strong> epibionts (green <strong>and</strong> red<br />

algae, bryozoans, polychaetes <strong>and</strong> bivalves). Only the oscular<br />

areas (from 1 to 4 cm in diameter) are free of these epibionts<br />

(Fig. 2A). In some cases, more than one individual of H.<br />

sonorensis was observed on a same specimen of Geodia, which<br />

was evident by their different tonality of coloration. Despite<br />

being interwoven, Haliclona was unattached in some areas,<br />

where we observed that the external tissue of Geodia did not<br />

seem to be damaged by the epizoic sponge (Fig. 2B, C). The<br />

area of G. media lacking epibionts has a rough texture due<br />

to the external layer of sterrasters (Fig. 2C, D), but the SEM<br />

showed that the megascleres (triaenes <strong>and</strong> oxeas) of G. media<br />

protrude the surface in the areas covered by Haliclona (Fig.<br />

2C, F) penetrating in the Haliclona sonorensis tissue (Fig.<br />

2D, E). There were spicules (oxeas) of H. sonorensis inside<br />

the ostias <strong>and</strong> embedded in the choanosome of G. media, <strong>and</strong><br />

there were also sterrasters of G. media in the choanosome of<br />

H. sonorensis.<br />

Haliclona sonorensis has been invariably found living on<br />

the surface of G. media which suggests that this species needs<br />

to live in association with G. media.<br />

Association Chalinula nematifera (de Laubenfels, 1954)<br />

– Pocillopora spp. Lamarck, 1816<br />

Material examined. A total of ten specimens of this<br />

association were collected <strong>between</strong> 3 <strong>and</strong> 12 m depth in<br />

three sites from Isabel Isl<strong>and</strong> (Bahía Tiburones, Playa Las<br />

Monas <strong>and</strong> Playa Iguanas), Nayarit, Mexico (28°52’20” N,<br />

112°02’01” W) (Fig. 1), from December 2003 to July 2006.<br />

Morphological description of the species in the association.<br />

The epizootic sponge has been identified as Chalinula<br />

nematifera (de Laubenfels, 1954). This is an encrusting<br />

sponge of violet color (1-4 mm thickness). This sponge grows<br />

only on live corals found in Isabel Isl<strong>and</strong> (Fig. 3). The surface<br />

is smooth to the naked eye, but it is punctated <strong>and</strong> shaggy in<br />

some places. Oscules are abundant, circular, from 4 to 6 mm


Fig. 1: Sampling localities<br />

(letters). The numbers indicate<br />

the site where specimens of each<br />

sponge association were collected:<br />

(1) two-sponge association, (2)<br />

sponge-alga association <strong>and</strong> (3)<br />

sponge-coral association.<br />

in diameter, <strong>and</strong> regularly distributed on the surface. They<br />

are situated at the summits of volcano-shaped elevations.<br />

Consistency is soft <strong>and</strong> spongy, somewhat elastic <strong>and</strong> slimy.<br />

The skeleton consists of oxeas: 87-(98)-112.5 x 2.5-(4.4)-5<br />

µm. Our specimens also show the characteristic pale threads<br />

through the body as described by de Laubenfels (1954),<br />

which presumably is a symbiotic fungus (WF Prud’homme<br />

van Reine, comments in de Weerdt 2002).<br />

The coral species on which C. nematifera was found<br />

were identified as Pocillopora damicornis Linnaeus, 1758,<br />

P. me<strong>and</strong>rina Dana, 1846, P. capitata Verrill, 1864 <strong>and</strong> P.<br />

verrucosa Ellis <strong>and</strong> Sol<strong>and</strong>er, 1786. In general, these coral<br />

species have characteristic shape because they form densely<br />

ramified colonies. They have calices crowded together over<br />

regularly-spaced wart-like projections (verrucae) (P. capitata<br />

<strong>and</strong> P. verrucosa).<br />

Description of the association. C. nematifera was found<br />

always on live ramified corals that live in areas exposed to<br />

light, most frequently with P. verrucosa (67%), <strong>and</strong> never on<br />

an<strong>other</strong> type of substratum. Nevertheless, it is possible to find<br />

these species of coral (mentioned above) without the sponge.<br />

149<br />

Approximately 17% of the Pocillopora colonies studied<br />

had C. nematifera in association. In these sponge/coral<br />

interactions, C. nematifera can cover branches partially or<br />

totally (5±5.12% of the total of branches of the colony), <strong>and</strong><br />

in all these cases we observed that the surface of the covered<br />

coral has no polyps. This sponge adhered firmly to the coral<br />

<strong>and</strong> is not easy to detach it from the substratum without<br />

breaking it. In fact, through the SEM images, we observed<br />

that the skeletal structure of the sponge seems to be cemented<br />

to the coral septa by spongin layers (Fig. 3C).<br />

Association Haliclona caerulea Hechtel, 1965 – Jania<br />

adherens Lamouroux, 1816<br />

Material examined. Sixteen specimens of the sponge-alga<br />

association were collected from ten sites from the Mazatlán<br />

Bay (23º13’49’’ N, 106º27’43’’ W), Sinaloa, Mexico (Fig. 1),<br />

<strong>between</strong> 2 to 6 m depth, from November 1997 until October<br />

2003.<br />

Morphological description of the species in the association.<br />

Haliclona (Gellius) caerulea is a massive sponge (from


150<br />

Fig. 2: Haliclona sonorensis<br />

– Geodia media association. A.<br />

two-sponge association containing<br />

several epibionts on its surface<br />

except on the osculate area.<br />

B. cross section of a specimen<br />

showing the Geodia surface almost<br />

totally covered by Haliclona<br />

sonorensis. D. SEM image<br />

showing the surface contact of the<br />

two interacting <strong>sponges</strong>, <strong>and</strong> C,<br />

E, F. the megascleres of Geodia<br />

protruding its ectosome, which are<br />

used as anchorage for the external<br />

sponge. The arrow in F shows<br />

an ostium of the internal sponge.<br />

Scale bars: A <strong>and</strong> B= 2 cm, C= 5<br />

mm, D= 500 µm, E= 200 µm, F=<br />

500 µm.<br />

3 to 13 cm high), white or beige in life <strong>and</strong> very brittle. The<br />

skeleton is constituted by oxeas (82.5-(177.3)-210 µm) <strong>and</strong><br />

sigmas (17.5-(21.6)-30 µm). The sponge has an unispicular<br />

ectosomal skeleton, formed by an isotropic tangential reticulation<br />

of oxeas, <strong>and</strong> the choanosomal skeleton is a somewhat<br />

confused reticulation of uni-multispicular primary <strong>and</strong> secondary<br />

lines that are difficult to appreciate because of their<br />

association with the alga (Fig. 4B).<br />

The alga was identified as Jania adherens Lamouroux,<br />

1816, which is an articulated erect red macroalga. The alga is<br />

pink with white joints, repeatedly branched, with a calcified<br />

thallus (from 0.4 to 0.5 mm diameter) except at the genicula.<br />

Description of the association. This sponge lives in intimate<br />

association with the red calcareous alga Jania adherens. The<br />

association consists of a massive <strong>and</strong> compact form where the<br />

sponge completely fills the spaces <strong>between</strong> the algal branches<br />

(Fig. 4A). The sponge generally covers the alga, <strong>and</strong> the algal<br />

branches very rarely protrude beyond the association surface.<br />

The morphology of the association is derived from the growth<br />

form of both organisms. Specimens of this association are lo-


Fig. 3: A. Chalinula nematifera –<br />

Pocillopora spp. association. B. C.<br />

nematifera tissue in close contact<br />

with the coral polyps (arrows). C.<br />

SEM image showing the skeletal<br />

structure of the sponge cemented<br />

to the coral septae (arrows). Scale<br />

bars A= 1 cm, B= 2000 µm, C =<br />

100 µm.<br />

cally abundant in rocky substrate environments (2-6 m depth),<br />

in areas of strong wave force. However, in these places, it is<br />

not possible to find the two species living in isolation, even<br />

though J. adherens lives in isolation in the intertidal zone.<br />

Jania adherens forms compact turfs approximately 2 cm high<br />

in the intertidal zone. However, in the subtidal zone (in association<br />

with H. caerulea) it reaches up to 13 cm in height. In<br />

the images obtained by SEM, we observed that the spicules<br />

of H. caerulea adhere firmly to the stalks of J. adherens by<br />

means of a fine spongin layer (Fig. 4C). We also observed that<br />

the primary lines of the sponge are partially replaced by the<br />

macroalgal thallus.<br />

Discussion<br />

Two-sponge association<br />

151<br />

Interactions among two or more <strong>sponges</strong> of different<br />

species, including cases of mutualism (Wilcox et al. 2002),<br />

parasitism (Wulff 1999) or space competition (Rützler 1970,<br />

Wulff 2006) have been previously recorded.<br />

A two-sponge association quite similar to ours was<br />

described recently from the Florida Keys (Wilcox et al.<br />

2002). In both cases, as it has also been documented for <strong>other</strong><br />

two-sponge associations (Sim 1998, Wilcox et al. 2002),


152<br />

Fig. 4: A. Haliclona caerulea<br />

– Jania adherens association.<br />

B. SEM images showing the<br />

skeletal structure of H. caerulea,<br />

which are partially substituted by<br />

the J. adherens branches in the<br />

association, <strong>and</strong> C. a close up of<br />

a spicule secondary line adhered<br />

to the algal thallus by means of a<br />

fine spongine layer. Scale bars A=<br />

1 cm, B= 300 µm, C= 60 µm.<br />

Haliclona sp. seems to be anchored on the protruding spicules<br />

of Geodia spp.<br />

There are studies that suggest that growth <strong>and</strong> survival<br />

increases when certain <strong>sponges</strong> of different species live in<br />

association, because they have different susceptibility to<br />

factors such as burial by sediment, fragmentation, predation<br />

<strong>and</strong> pathogens (Wulff 1997a, 1999, Engel <strong>and</strong> Pawlik 2005,<br />

Wulff 2006). However, in the association from the Florida<br />

Keys, it was suggested that it could be a mutualistic <strong>and</strong><br />

obligatory symbiosis, where the external sponge protects<br />

its host from the predation, while Geodia sp. offers it a sure<br />

substratum for its survival (Wilcox et al. 2002).<br />

However, it is interesting to comment that the Caribbean<br />

sponge Geodia gibberosa is chemically undefended against<br />

turtle <strong>and</strong> fish predation (Dunlap <strong>and</strong> Pawlik 1996, 1998), <strong>and</strong><br />

uses its chemical products to attract fouling organisms. This<br />

could resemble Geodia sp. in association with Haliclona sp.<br />

(Wilcox et al. 2002), since one of the benefits acquired by the<br />

sponge Geodia cydonium fouled by the red alga Rytyphlöea<br />

tinctoria is the protection against the adverse effects of<br />

ultraviolet radiation, allowing the specimens to live under<br />

illuminated habitats (Mercurio et al. 2006).<br />

It is possible that an obligatory relationship also exists<br />

<strong>between</strong> H. sonorensis <strong>and</strong> G. media, at least for H.<br />

sonorensis, since it has not been found in isolation within the<br />

environment where the associations are encountered. In fact,<br />

the high specificity of Haliclona to live with Geodia is very<br />

interesting because this association does not originate in a<br />

highly space-competitive environment like reef ecosystems,<br />

<strong>and</strong> therefore it could not be a simple case of epizoism due<br />

to space limitation (Rützler 1970). In addition, it is important<br />

to mention that there is no evidence of tissue damage on the<br />

surface of G. media covered by H. sonorensis, as it has been<br />

documented in <strong>other</strong> two-sponge interactions (Thacker et al.<br />

1998). Although we did not make experiments to test whether<br />

a benefit exists <strong>between</strong> G. media <strong>and</strong> H. sonorensis, bioactive<br />

natural products have been described in G. media from the<br />

Sea of Cortes (Pettit et al. 1981, Pettit et al. 1990), that could<br />

attract fouling organisms, similar to Geodia gibberosa (Engel<br />

<strong>and</strong> Pawlik 2000, Engel <strong>and</strong> Pawlik 2005).<br />

In the association described here, one or more specimens<br />

of H. sonorensis are found attached to the same G. media<br />

specimen, establishing contact but without fusing. These<br />

observations support the idea that this sponge most likely<br />

colonizes G. media through larval settlement, in order to<br />

obtain an appropriate substratum for its survival (Wulff<br />

1997b, Wilcox et al. 2002).<br />

Sponge-coral association<br />

Sponge-coral interactions are common in coral reefs where<br />

strong competition for space exists <strong>and</strong> where it is frequent<br />

that aggressive <strong>sponges</strong> overgrow the coral (Aerts 1998).<br />

The sponge Chalinula nematifera has been described<br />

previously overgrowing hard corals in reefs from the West-<br />

Central Pacific (de Laubenfels 1954). Surprisingly, this species<br />

also seems to be specifically attracted to pocilloporid corals<br />

from the Sea of Cortes, since it has not been found colonizing<br />

<strong>other</strong> types of substratum. Nevertheless, the species of coral<br />

associated with this sponge can be found in an isolated form.<br />

This suggests that it could be an obligatory relationship for<br />

the sponge, <strong>and</strong> facultative for the host (Pocillopora spp.).<br />

We also suggest that this relationship can have negative<br />

outcome for the coral, since the sponge seems to be killing the<br />

coral tissue, similar to what has been documented for several<br />

sponge/coral interactions (Jackson <strong>and</strong> Buss 1975, Plucer-<br />

Rosario 1987, Macintyre et al. 2000, Aerts 2000, Rützler<br />

2002, de Voogd et al. 2004, Coles <strong>and</strong> Bolick 2006, Gochfeld


et al. 2006). However, we do not know if C. nematifera uses<br />

chemical products to kill the coral polyps (Nishiyama <strong>and</strong><br />

Bakus 1999) or if it simply sm<strong>other</strong>s them (Wulff 1999).<br />

Some authors have suggested that the ability of <strong>sponges</strong><br />

to overgrow corals appears to depend on their growth rate<br />

<strong>and</strong> form (Aerts 2000). For example, in the sponge Terpios<br />

hoshinota, it was suggested that its success to overgrow large<br />

extensions of live corals is due to a fast spreading rate, aided<br />

by fast asexual propagation (fragmentation) (Plucer-Rosario<br />

1987, Rützler <strong>and</strong> Muzik 1993).<br />

Chalinula nematifera possibly finds a substratum that<br />

offers multiple protected microhabitats in pocilloporid corals,<br />

since they are densely ramified species which are often used<br />

as microhabitats by several organisms (Patton 1974). Thus,<br />

C. nematifera could likely benefit by finding an appropriate<br />

substratum that offers protection against environmental<br />

factors (e.g. UV radiation, sedimentation <strong>and</strong>/or predation).<br />

This is an advantage that it could not find with the <strong>other</strong><br />

non-branched coral species (Porites, Psammocora, Pavona<br />

<strong>and</strong> Fungia) that inhabit the same site as the C. nematifera/<br />

Pocillopora spp. association, most likely because they do not<br />

offer this kind of physical protection.<br />

Although in most of the sponge-coral interactions that<br />

have been described, it has been found that these <strong>relationships</strong><br />

seem to be negative for the coral (de Voogd et al. 2004, Coles<br />

<strong>and</strong> Bolick 2006, Gochfeld et al. 2006, López-Victoria et al.<br />

2006), there are also documented cases of mutualisms; for<br />

example, the sponge Mycale laevis Carter 1882 which is<br />

found encrusting on the lower surfaces of flattened reef corals<br />

(mainly on Montastrea annularis) in the Caribbean Sea. M.<br />

laevis benefits by colonizing a substrate that is free from <strong>other</strong><br />

sessile organisms. In turn, the coral benefits from an increased<br />

feeding efficiency as a result of water currents produced by<br />

the sponge <strong>and</strong> it is protected from invasion by boring <strong>sponges</strong><br />

(Goreau <strong>and</strong> Hartman 1966). In the case of sponge/octocoral<br />

associations, the sponge generally obtains structural support<br />

from its partner <strong>and</strong> the octocoral obtains protection against<br />

predation (van Soest 1987, Calcinai et al. 2004). In addition,<br />

it has been documented that both organisms also benefit by<br />

increasing their dispersal capacity (Calcinai et al. 2004).<br />

Sponge-alga association<br />

Associations <strong>between</strong> <strong>sponges</strong> <strong>and</strong> photosynthetic<br />

organisms are important not only for the partners, but also<br />

for the ecosystem they inhabit, because they can contribute<br />

significantly to the primary productivity, mainly in<br />

oligothrophic ecosystems (Wilkinson 1983, Steindler et al.<br />

2002). One of the most-studied sponge/macroalga symbioses<br />

is the Haliclona cymaeformis/Ceratodictyon spongiosum<br />

association (from the Great Barrier Reef, Australia)<br />

(Trautman et al. 2000, Trautman <strong>and</strong> Hinde 2002, Davy et<br />

al. 2002), which we could consider as a “sibling” association<br />

of the H. caerulea/J. adherens association described here.<br />

In both cases the mutualistic association derives similar<br />

benefits for the partners (such as protection against physical<br />

disturbances, structural support, high dispersal capacity<br />

through fragmentation), <strong>and</strong> in both cases the sponge is a<br />

species of Haliclona that lives associated with a red macroalga<br />

(Trautman et al. 2000, Trautman <strong>and</strong> Hinde 2002, Carballo<br />

153<br />

<strong>and</strong> Ávila 2004, Carballo et al. 2006). However, in spite of<br />

the similarities of these two interactions, the H. caerulea/<br />

J. adherens association does not live in an oligotrophic<br />

environment in the Bay of Mazatlán (see Carballo 2006).<br />

Our investigations into the H. caerulea-Jania adherens<br />

association suggests that this is an obligatory <strong>and</strong> mutualistic<br />

association, where both organisms benefit by increased growth,<br />

widespread their distribution area toward an environment<br />

where none can inhabit by itself, <strong>and</strong> by the acquisition of<br />

a structural support that gives them bigger rigidity than their<br />

free-living form (Ávila <strong>and</strong> Carballo 2004, Carballo <strong>and</strong> Ávila<br />

2004, Carballo et al. 2006). H. caerulea can also substitute<br />

part of its skeletal structure (mainly primary lines) with the<br />

branches of J. adherens, reducing the investment in spicule<br />

production (Carballo et al. 2006), as it has been documented<br />

in <strong>other</strong> sponge symbioses (de Laubenfels 1950, Vacelet<br />

1981, Rützler 1990, Uriz et al. 1992). In addition, it has been<br />

demonstrated that H. caerulea in association with J. adherens<br />

(from the Pacific coast of Panama) acquires the benefit of<br />

being protected against fish predation (Wulff 1997a).<br />

On the <strong>other</strong> h<strong>and</strong>, H. caerulea has never been found<br />

in isolated form at the depth range where the sponge-alga<br />

association lives in the Bay of Mazatlán, because it has a very<br />

fragile structure, <strong>and</strong> it is unable to live in that environment,<br />

which is characterized by strong water movement (Carballo<br />

et al. 2006). Although this association reproduces mainly by<br />

fragmentation, larval settlements of H. caerulea have been<br />

registered in the intertidal zone where J. adherens inhabits in<br />

isolated form (Ávila <strong>and</strong> Carballo 2006). In fact, laboratory<br />

experiments demonstrated that the larvae of H. caerulea can<br />

select J. adherens as substratum while rejecting <strong>other</strong>s (Ávila<br />

<strong>and</strong> Carballo 2006), probably because the alga fronds offer<br />

a shady <strong>and</strong> tangled microrefuge, which could increase the<br />

post-settlement survival (Buss 1979, Maldonado <strong>and</strong> Uriz<br />

1998).<br />

On the <strong>other</strong> h<strong>and</strong>, it is important to add that this association<br />

has also been found in <strong>other</strong> localities in Mexico, such as<br />

Tuxpan, Veracruz (in the Gulf of Mexico) <strong>and</strong> Manzanillo,<br />

Colima <strong>and</strong> Huatulco, Oaxaca (in the Mexican Pacific)<br />

(personal observations).<br />

The diversity of associations among the haplosclerid<br />

<strong>sponges</strong><br />

The three symbiotic <strong>sponges</strong> (H. sonorensis, C. nematifera<br />

<strong>and</strong> H. caerulea) described in this study belong to the order<br />

Haplosclerida, which is one of the most diverse groups of the<br />

phylum <strong>Porifera</strong> (Hooper <strong>and</strong> van Soest 2002). Upon revising<br />

the literature, we have found that most of the <strong>sponges</strong> (21%<br />

of 248 cases) that have been previously recorded establishing<br />

associations with <strong>other</strong> taxa (see introduction), belong to the<br />

order Haplosclerida, <strong>and</strong> mostly to the family Chalinidae<br />

(50% of 51 registrations) (Fig. 5) (Dauer 1974, Vacelet 1981,<br />

Ellison et al. 1996, Garson et al. 1998, Ilan et al. 1999, Vacelet<br />

et al. 2001, Steindler et al. 2002, Wilcox et al. 2002, among<br />

<strong>other</strong>s). These associations have been recorded mainly in<br />

shallow tropical <strong>and</strong> subtropical environments (such as coral<br />

reefs), which are characterized by a high competition for<br />

space <strong>and</strong> food by the organisms that inhabit there. It seems<br />

that some <strong>sponges</strong> have probably “learned” to associate with


154<br />

Fig. 5: A. <strong>Symbiotic</strong> associations<br />

<strong>between</strong> <strong>sponges</strong> <strong>and</strong> <strong>other</strong><br />

organisms registered in the<br />

different orders of the class<br />

Demospongiae <strong>and</strong> B. in the order<br />

Haplosclerida.<br />

<strong>other</strong> organisms that offer them some kind of protection<br />

against environmental factors (such as fish predation,<br />

sedimentation, UV radiation, tissue resistance). For example,<br />

in the Geodia sp./Haliclona sp. association, it has been<br />

suggested that Geodia sp. is chemically defended against fish<br />

predation <strong>and</strong> protected from sedimentation by the sponge<br />

partner (Wilcox et al. 2002). In an<strong>other</strong> haploclerid species<br />

such as Haliclona cymaeformis <strong>and</strong> Haliclona implexiformis<br />

that live associated with photosynthetic organisms (macroalga<br />

<strong>and</strong> mangrove respectively), it has been demonstrated that<br />

nutrient translocation also exists <strong>between</strong> the sponge <strong>and</strong><br />

its host (Ellison et al. 1996, Davy et al. 2002). In the case<br />

of species that shelter cyanobacteria (e.g. Adocia atra <strong>and</strong><br />

Haliclona debilis) in their tissue, it has been suggested that<br />

they can benefit by protecting their surface from UV-radiation<br />

<strong>and</strong>/or obtain an alternative source of food (Rützler 1990,<br />

Steindler et al. 2002). It has also been suggested that they<br />

reinforce their skeletal structure using their partner to avoid<br />

being broken into fragments by the current, as is the case<br />

of H. caerulea (Carballo et al. 2006) <strong>and</strong> H. cymaeformis<br />

(Trautman <strong>and</strong> Hinde 2002).<br />

On the <strong>other</strong> h<strong>and</strong>, there are many bioactive compounds<br />

known in haplosclerid <strong>sponges</strong> (Frincke <strong>and</strong> Faulkner<br />

1982, Isaacs <strong>and</strong> Kashman 1992, van Soest <strong>and</strong> Braekman<br />

1999), which can also be used for different purposes such as<br />

antifoulants (Sera et al. 2002), as antimicrobial compounds<br />

(Xue et al. 2004, Ely et al. 2004) or in competition for space<br />

(Nishiyama <strong>and</strong> Bakus 1999).<br />

Conclusions<br />

In general, it seems that in the sponge/sponge <strong>and</strong><br />

sponge/macroalga associations the <strong>relationships</strong> are usually<br />

mutualistic, or at least no type of damage has been evidenced<br />

among the associated organisms. In contrast, in most of the<br />

non-boring <strong>sponges</strong> associated to ramified corals that have<br />

been described (including C. nematifera/Pocillopora spp.<br />

association), the relationship seems to be negative for the coral<br />

species. Nevertheless, it is necessary to do more experimental<br />

<strong>and</strong> population dynamics studies of these associations in<br />

order to underst<strong>and</strong> more about the complexity of their life<br />

history <strong>and</strong> their ecological importance in the ecosystem they<br />

inhabit.<br />

Acknowledgements<br />

We are grateful to the following sources of funding: CONABIO<br />

FB666/S019/99, CONABIO FB789/AA004/02, CONABIO<br />

DJ007/26 <strong>and</strong> CONACYT SEP-2003- C02-42550. This work<br />

was carried out under permission of SAGARPA (Permit numbers:<br />

DGOPA.02476.220306.0985 <strong>and</strong> DGOPA.06648.140807.3121).<br />

We thank Clara Ramírez, Pedro Allende <strong>and</strong> Victoria Montes for<br />

help with the literature <strong>and</strong> images, German Ramírez <strong>and</strong> Carlos<br />

Suárez for their computer assistance, Cayetano Robles, Gonzalo<br />

Pérez <strong>and</strong> Cristina Vega for their assistance in the field sampling,<br />

<strong>and</strong> the Director Parque Nacional Isla Isabel Jorge Castrejón for the<br />

availability <strong>and</strong> the permission conferred for the collection of the<br />

samples in Isabel isl<strong>and</strong>.


References<br />

Aerts LAM (1998) Sponge/coral interactions in Caribbean reefs:<br />

analysis of overgrowth patterns in relation to species identity <strong>and</strong><br />

cover. Mar Ecol Prog Ser 175:241-249<br />

Aerts LAM (2000) Dynamics behind st<strong>and</strong>off interactions in three<br />

reef sponge species <strong>and</strong> the coral Montastraea cavernosa. PSZN<br />

Mar Ecol 21: 191-204<br />

Ávila E, Carballo JL (2004) Growth <strong>and</strong> st<strong>and</strong>ing stock biomass of<br />

a mutualistic association <strong>between</strong> the sponge Haliclona caerulea<br />

<strong>and</strong> the red alga Jania adherens. Symbiosis 36(3): 225-244<br />

Ávila E, Carballo JL (2006) Habitat selection by larvae of<br />

the symbiotic sponge Haliclona caerulea (Hechtel, 1965)<br />

(Demospongiae, Haplosclerida). Symbiosis 41: 21-29<br />

Buss LW (1979) Bryozoan overgrowth interactions-the<br />

interdependence of competition for space <strong>and</strong> food. Nature 281:<br />

475-477<br />

Calcinai B, Bavestrello G, Cerrano C (2004) Dispersal <strong>and</strong><br />

association of two alien species in the Indonesian coral reefs:<br />

the octocoral Carijoa riisei <strong>and</strong> the demosponge Desmapsamma<br />

anchorata. J Mar Biol Assoc UK 84: 937-941<br />

Carballo JL (2006) Effect of natural sedimentation on the structure<br />

of tropical rocky sponge assemblages. Ecoscience 13: 119-130<br />

Carballo JL, Ávila E (2004) Population dynamics of a mutualistic<br />

interaction <strong>between</strong> the sponge Haliclona caerulea, <strong>and</strong> the red<br />

alga Jania adherens. Mar Ecol Prog Ser 279: 93-104<br />

Carballo JL, Ávila E, Enríquez S, Camacho L (2006) Phenotypic<br />

plasticity in a mutualistic association <strong>between</strong> the sponge Haliclona<br />

caerulea <strong>and</strong> the calcareous macroalga Jania adherens induced<br />

by transplanting experiments. I: morphological responses of the<br />

sponge. Mar Biol 148: 467-478<br />

Coles SL, Bolick H (2006) Assessment of invasiveness of the orange<br />

keyhole sponge Mycale armata in Kâne’ohe Bay, O’ahu, Hawai’i.<br />

7 th Int Sponge Symp (abstract) pp. 110<br />

Cruz-Barraza JA, Carballo JL (2006) A new species of Haliclona<br />

(Demospongiae: Haplosclerida) living in association with Geodia<br />

media Bowerbank (Mexican Pacific coast). Zootaxa 1343: 43-54<br />

Davy SK, Trautman D, Borowitzka MA, Hinde R (2002) Ammonium<br />

excretion by a sponge <strong>and</strong> its ecological importance in a spongerhodophyte<br />

symbiosis. J Exp Biol 205: 3505-3511<br />

Dauer DM (1974) Polychaete fauna associated with Gulf of Mexico<br />

<strong>sponges</strong>. Florida Scientist 36: 192-196<br />

de Laubenfels MW (1950) The <strong>sponges</strong> of Kaneohe Bay, Oahu. Pac<br />

Sci 4(1): 3-36<br />

de Laubenfels MW (1954) The <strong>sponges</strong> of the west-central Pacific.<br />

Oreg St Monogr Zool 7: 1-306<br />

de Voogd N, Becking LE, Hoeksema BW, Noor A, van Soest<br />

RWM (2004) Sponge interactions with spatial competitors in the<br />

Spermonde Archipelago. In: Pansini M, Pronzato R, Bavestrello<br />

G, Manconi R (eds). Sponge science in the new millennium. Boll<br />

Mus Ist Biol Univ Genova 68: 253-261<br />

de Weerdt WH (2002) Family Chalinidae Gray. In: Hooper JNA, van<br />

Soest RWM (eds). Systema <strong>Porifera</strong>: a guide to the classification<br />

of <strong>sponges</strong>. Kluwer Academic/Plenum Publishers, New York. pp.<br />

852-873<br />

Dunlap M, Pawlik JR (1996) Video-monitored predation by<br />

Caribbean reef fishes on an array of mangrove <strong>and</strong> reef <strong>sponges</strong>.<br />

Mar Biol 126: 117-123<br />

Dunlap M, Pawlik JR (1998) Spongivory by parrotfish in Florida<br />

mangrove <strong>and</strong> reef habitats. PSZN Mar Ecol 19: 325-337<br />

155<br />

Ellison AM, Farnsworth EJ, Twilley RR (1996) Facultative<br />

mutualism <strong>between</strong> red mangroves <strong>and</strong> root-fouling <strong>sponges</strong> in<br />

Belizean mangal. Ecology 77(8): 2431-2444<br />

Ely R, Supriya T, Naik CG (2004) Antimicrobial activity of marine<br />

organisms collected off the coast of South East. India. J Exp Mar<br />

Biol Ecol 309: 121-127<br />

Engel S, Pawlik JR (2000) Allelopathic activities of sponge extracts.<br />

Mar Ecol Prog Ser 207: 273-281<br />

Engel S, Pawlik JR (2005) Interactions among Florida <strong>sponges</strong>. II.<br />

Mangrove habitats. Mar Ecol Prog Ser 303: 145-152<br />

Frincke JM, Faulkner DJ (1982) Antimicrobial metabolites of the<br />

sponge Reniera sp. J Am Chem Soc 104: 265-269<br />

Frost TM, Williamson CE (1980) In situ determination of the<br />

effect of symbiotic algae on the growth of the freshwater sponge<br />

Spongilla lacustris. Ecology 61: 1361-1370<br />

Gaino E, Lancioni T, La Porta G, Todini B (2004) The consortium<br />

of the sponge Ephydatia fluviatilis (L.) living on the common<br />

reed Phragmites australis in Lake Piediluco (central Italy).<br />

Hydrobiologia 520: 175-178<br />

Gaino E, Sarà M (1994) Siliceous spicules of Tethya seychellensis<br />

(<strong>Porifera</strong>) support the growth of a green alga: A possible light<br />

conducting system. Mar Ecol Prog Ser 108: 147-151<br />

Garson MJ, Flowers AE, Webb RI, Charan RD, McCaffrey EJ (1998)<br />

A sponge/dinoflagellate association in the haplosclerid sponge<br />

Haliclona sp.: cellular origin of cytotoxic alkaloids by Percoll<br />

density gradient fractionation. Cell Tissue Res 293: 365-373<br />

Gochfeld D, Harrison L, Olson J, Lesser MP, Ankisetty S, Slattery M<br />

(2006) Allelopathic effects of the Caribbean sponge Svenzea zeai<br />

on the coral Montastrea annularis. In: Custódio MR, Lôbo-Hajdu<br />

G, Hajdu E, Muricy G (eds). 7 th International Sponge Symposium -<br />

Book of Abstracts (Armação dos Búzios, Brazil). Museu Nacional,<br />

Série Livros, vol. 16. pp. 116<br />

Goreau TF, Hartman WD (1966) Sponge: effect on the form of reef<br />

corals. Science 151: 343-344<br />

Henkel TO, Pawlik JR (2005) Habitat use by sponge-dwelling<br />

brittlestars. Mar Biol 146: 301-313<br />

Hooper NA, van Soest RWM (2002) Systema <strong>Porifera</strong>: a guide to the<br />

classification of <strong>sponges</strong>. Kluwer Academic, Plenum Publishers,<br />

New York<br />

Ilan M, Loya Y, Kolbasov GA, Brickner I (1999) Sponge inhabiting<br />

barnacles on coral reefs. Mar Biol 133: 709-716<br />

Isaacs S, Kasbman Y (1992) Shaagrockol B <strong>and</strong> C; two<br />

hexaprenylhydroquinone disulfates from the Red Sea sponge<br />

Toxiclona toxius. Tetrahedron Lett 33: 2227-2230<br />

Jackson JBC, Buss L (1975) Allelopathy <strong>and</strong> spatial competition<br />

among coral reef invertebrates. Proc Natl Acad Sci 72: 5160-5163<br />

Kohler KE, Gill SM (2006) Coral Point Count with Excel extensions<br />

(CPCe): A Visual Basic program for the determination of coral <strong>and</strong><br />

substrate coverage using r<strong>and</strong>om point count methodology. Comp<br />

Geosci 32: 1259-1269<br />

López-Victoria M, Zea S, Weil E (2006) Competition for space<br />

<strong>between</strong> encrusting excavating Caribbean <strong>sponges</strong> <strong>and</strong> <strong>other</strong> coral<br />

reef organisms. Mar Ecol Prog Ser 312: 113-121<br />

Macintyre IG, Precht WF, Aronson RB (2000) Origin of the Pelican<br />

Cays ponds, Belize. Atoll Res Bull 466: 1-11<br />

Magnino G, Gaino E (1998) Haplosyllis spongicola (Grübe)<br />

(Polychaeta, Syllidae) associated with two species of <strong>sponges</strong> from<br />

East Africa (Tanzania, Indian Ocean). PSZN Mar Ecol 19: 77-87


156<br />

Maldonado M, Uriz MJ (1998) Microrefuge exploitation by subtidal<br />

encrusting <strong>sponges</strong>: patterns of settlement <strong>and</strong> post-settlement<br />

survival. Mar Ecol Prog Ser 174: 141-150.<br />

Mercurio M, Corriero G, Gaino E (2006) Sessile <strong>and</strong> non-sessile<br />

morphs of Geodia cydonium (Jameson) (<strong>Porifera</strong>, Demospongiae)<br />

in two semi-enclosed Mediterranean bays. Mar Biol 148: 489-501<br />

Meroz E, Ilan M (1995) Cohabitation of a coral reef sponge <strong>and</strong> a<br />

scyphozoan. Mar Biol 124: 453-459<br />

Nishiyama GK, Bakus GK (1999) Release of allelochemicals by<br />

three tropical <strong>sponges</strong> (Demospongiae) <strong>and</strong> their toxic effects on<br />

coral substrate competitors. Memoir Queensl Mus 44: 411-417<br />

Palumbi SR (1985) Spatial variation in an algal-sponge<br />

commensalism <strong>and</strong> the evolution of ecological interactions. Am<br />

Nat 126: 267-274<br />

Patton WK (1974) Community structure among the animals<br />

inhabiting the coral Pocillopora damicornis at Heron Isl<strong>and</strong>,<br />

Australia. Bull Mar Sci 14(2): 212-243<br />

Pettit GR, Rideout JA, Hasler JA (1981) Isolation of geodiastatins<br />

1 <strong>and</strong> 2 from the marine sponge Geodia mesotriaena. J Nat Prod<br />

44(5): 588-92<br />

Pettit GR, Rideout JA, Hasler JA (1990) Isolation of geodiatoxins<br />

2 <strong>and</strong> 4 from the marine sponge Geodia mesotriaena. Comp Bio<br />

Physiol Part C 96(2): 305-6<br />

Plucer-Rosario G (1987) The effect of substratum on the growth of<br />

Terpios, an encrusting sponge which kills corals. Coral Reefs 5(4):<br />

197-200<br />

Rützler K (1970) Spatial competition among <strong>Porifera</strong>: solution by<br />

epizoism. Oecologia 5: 85-95<br />

Rützler K (1974) The burrowing <strong>sponges</strong> of Bermuda. Smithson<br />

Contrib Zool 165:1-32<br />

Rützler K (1990) Associations <strong>between</strong> Caribbean <strong>sponges</strong> <strong>and</strong><br />

photosynthetic organisms. In: Rützler K (ed). New perspectives<br />

in sponge biology. Smithsonian Institution Press, Washington DC.<br />

pp. 455-466<br />

Rützler K (2002) Impact of crustose clionid <strong>sponges</strong> on Caribbean<br />

Reef corals. Acta Geol Hisp 37: 61-72<br />

Rützler K, Muzik K (1993) Terpios hoshinota, a new<br />

cyanobacteriosponge threatening Pacific reefs. In: Uriz MJ, Rützler<br />

K (eds). Recent Advances in Ecology <strong>and</strong> Systematics of Sponges.<br />

Sci Mar 57(4): 395-403<br />

Sarà M, Vacelet (1973) Écologie des Démo<strong>sponges</strong>. In: Grassé PP<br />

(ed). Spongiaires. Anatomie, Physiologie, Systématique, Écologie.<br />

Masson de Cie, Paris. pp. 462-576<br />

Schuchert P (2003) Hydroids (Cnidaria, Hydrozoa) of the Danish<br />

expedition to the Kei Isl<strong>and</strong>s. Steenstrupia 27: 137-256<br />

Sera Y, Adachi K, Fujii K, Shizuri Y (2002) Isolation of<br />

Haliclonamides: New peptides as antifouling substances from a<br />

marine sponge species, Haliclona. Mar Biotechnol 3: 441-446<br />

Sim CJ (1998) Two-sponge association from Komun Isl<strong>and</strong>,<br />

Korea. In: Watanabe Y, Fusetani, N (eds). Sponge sciences:<br />

multidisciplinary perspectives. Springer-Verlag, Tokyo. pp 109-<br />

117<br />

Steindler L, Beer S, Ilan M (2002) Photosymbiosis in intertidal <strong>and</strong><br />

subtidal tropical <strong>sponges</strong>. Symbiosis 33:263-273<br />

Thacker RW, Becerro MA, Lumbang WA, Paula VJ (1998)<br />

Allelopathic interactions <strong>between</strong> <strong>sponges</strong> on a tropical reef.<br />

Ecology 79(5): 1740-1750<br />

Thakur NL, Müller WEG (2004) Biotechnological potential of<br />

marine <strong>sponges</strong>. Curr Sci 86(11): 1506-1512<br />

Trautman DA, Hinde R, Borowitzka MA (2000) Population<br />

dynamics of an association <strong>between</strong> a coral reef sponge <strong>and</strong> a red<br />

macroalga. J Exp Mar Biol Ecol 244: 87-105<br />

Trautman DA, Hinde R (2002) Sponge/algal symbioses: a diversity<br />

of associations. In: Seckbach J (ed). Symbiosis: Mechanisms <strong>and</strong><br />

Model Systems. Kluwer Academic Publishers, Netherl<strong>and</strong>s, 796<br />

pp.<br />

Uriz MJ, Rosell D, Maldonado M (1992) Parasitism, comensalism<br />

or mutualism? The case of Scyphozoa (Coronatae) <strong>and</strong> horny<br />

<strong>sponges</strong>. Mar Ecol Prog Ser 81: 247-255<br />

Vacelet J (1981) Algal-sponge symbioses in the coral reefs of New<br />

Caledonia: a morphological study. Proc 4 th Int Coral Reef Symp,<br />

Manila 2: 713-719<br />

Vacelet J, Sofyani AA, Lihaibi SA, Kornprobst JM (2001) A new<br />

haplosclerid sponge species from the Red Sea. J Mar Biol Assoc<br />

UK 81: 943-948<br />

van Soest RWM, Braekman JC (1999) Chemosystematics of<br />

<strong>Porifera</strong>: a review. Memoir Queensl Mus 44: 569-589<br />

West DA (1979) <strong>Symbiotic</strong> zoanthids (Anthozoa: Cnidaria) of<br />

Puerto Rico. Bull mar Sci 29: 253-271.<br />

Wilcox TP, Hill M, DeMeo K (2002) Observations on a new twosponge<br />

symbiosis from the Florida Keys. Coral Reefs 21: 198-<br />

204<br />

Wilkinson CR (1983) Net primary productivity of coral reef <strong>sponges</strong>.<br />

Science 219: 410-412<br />

Wulff JL (1997a) Causes <strong>and</strong> consequences of differences in <strong>sponges</strong><br />

diversity <strong>and</strong> abundance <strong>between</strong> the Caribbean <strong>and</strong> eastern Pacific<br />

at Panama. Proc 8 th Int Coral Reef Symp, Panama 2: 1377-1382<br />

Wulff JL (1997b) Mutualisms among species of coral reef <strong>sponges</strong>.<br />

Ecology 78: 146-159<br />

Wulff JL (1999) A sponge that cheats on diffuse mutualism among<br />

<strong>other</strong> sponge species. Mem Qld Mus 44: 686<br />

Wulff JL (2006) Ecological interactions of marine <strong>sponges</strong>. Can J<br />

Zool 84: 146-166<br />

Xue S, Zhanga HT, Wua PC, Zhanga W, Yuan Q (2004) Study on<br />

bioactivity of extracts from marine <strong>sponges</strong> in Chinese Sea. J Exp<br />

Mar Biol Ecol 298: 71-78

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