Abstract
The cheilostome bryozoan Antarctothoa bougainvillei (d’Orbigny) is the most frequent epibiont on the ribbon-like red alga Hymenena laciniata (Hooker f. & Harvey) Kylin in San Sebastián Bay (Tierra del Fuego, Argentina). Twenty-one thalli and 1,484 colonies were examined to analyse the relationship between both species. In most cases, number and area of colonies did not differ significantly at both sides of the thallus. Ancestrulae (i.e., founder zooids originating colonies by asexual budding) were mostly oriented facing the algal growing edge. Colonies were more frequent on central than on marginal zones of the thalli. The population of A. bougainvillei was mainly composed of very small colonies (<10 mm2). Larger colonies predominated and intraspecific competition was more intense near the basal portions of the thalli. Fecundity (number of ovicells) increased at a significantly higher rate in colonies with margins obstructed by conspecific neighbours than in free-growing colonies. Colonies were significantly larger on somatic than on reproductive algal tissues. As total and reproductive surfaces covered by colonies of A. bougainvillei were on average very low (4.43% and 0.53%, respectively), this epibiont is not supposed to produce a negative effect on H. laciniata.
Similar content being viewed by others
Avoid common mistakes on your manuscript.
Introduction
Algae are a suitable substratum for many epibionts, including bryozoans (Rogick & Croasdale, 1949; Ryland, 1962; Winston & Eiseman, 1980; Seed & O’Connor, 1981). An epibiotic association, however, creates a complex network of benefits and disadvantages between epibiont and basibiont (Wahl, 1989). Encrusting bryozoans increase frond loss (Dixon et al., 1981), decrease the photosynthetic rate and photon-flux density and affect the quality of the incident light reaching the thallus (Cancino et al., 1987; Muñoz et al., 1991). The plant may react by altering the relative concentration of photosynthetic pigments to compensate the reduction of incident light (Molina et al., 1991; Muñoz et al., 1991). In addition, CO2 released from bryozoan cells may be used by the alga as a source of photosynthetic inorganic carbon (Muñoz et al., 1991; Mercado et al., 1998). Epibionts may as well benefit from substances produced by the basibiont, e.g., colonial survivorship and percentage of non-degenerated zooids are enhanced in bryozoan colonies which were allowed to absorb algal exudates (Manríquez & Cancino, 1996).
Algae possess different mechanical and chemical means to deter the settlement of fouling organisms (Dworjanyn et al., 1999, 2006; Nylund & Pavia, 2005). To maximize survival on these ephemeral substrata, solitary and colonial organisms show essentially different abilities to use space (Jackson, 1977). While both are able to select habitat during settlement, only colonial animals exhibit directional growth towards more favourable refuges on the substratum (Buss, 1979).
Bryozoan colonies are not randomly distributed on algae. In choice experiments, larvae show clear preferences related to the observed natural distribution of the adults (Ryland, 1959). Settlement mainly occurs on certain regions (Hayward & Harvey, 1974a) or on younger parts of the fronds (Stebbing, 1972), where life expectancy of the colonies is maximized (Cancino, 1986). Asexual budding of zooids may continue until the substratum is completely covered by a mosaic of colonies (Hayward & Ryland, 1975), whose fecundity is linearly related to colony area (Hayward, 1973). Crowding by conspecifics was experimentally shown to trigger the onset of sexual maturity (Harvell & Grosberg, 1988; Cancino et al., 1991; Harvell & Helling, 1993), but aggregation of colonies seems to have no effect on growth and mortality rates (Hayward & Harvey, 1974b). Studies analysing the orientation of bryozoan ancestrulae, i.e., founder zooids originating colonies by asexual budding, showed that they are mainly aligned parallel to the median axis of the frond, facing the growing tip (Ryland & Stebbing, 1971; Ryland, 1974a, b, 1977).
Most investigations on the distribution, demography and competitive interactions of epiphytic bryozoans, however, dealt with assemblages growing on brown algae (Stebbing, 1972, 1973; Hayward, 1973; Ryland, 1974a; Hayward & Ryland, 1975; Cancino, 1986; among others). Since different algal taxa show a vast array of chemical and mechanical defences to deter herbivory (Hay & Fenical, 1988; Hay, 1991) and fouling (Dworjanyn et al., 1999, 2006; Nylund & Pavia, 2005), it should be interesting to test whether these patterns occur also on the surface of red algae.
The abundance of Antarctothoa bougainvillei (d’Orbigny) (=Celleporella bougainvillei, see Wright et al., 2007), a common encrusting cheilostome bryozoan in Magellanic and Antarctic coastal environments (López Gappa, 1985; Moyano, 1986; Hayward, 1995; Linse et al., 2006), gave us the opportunity to analyse the spatial pattern of its colonies on the ribbon-like thalli of the red alga Hymenena laciniata (Hooker f. & Harvey) Kylin. In the present study, we investigated: (1) how much of the algal surface and reproductive structures are covered by the bryozoan, (2) the relationship between intraspecific competition and fecundity in colonies of A. bougainvillei, (3) whether colonies are randomly scattered or show any preference for different areas of the algal thallus and (4) whether ancestrulae exhibit a clear orientation or are randomly placed with respect to the frond axis.
Materials and methods
Thalli of Hymenena laciniata are erect, mostly monostromatic, up to 25-cm tall, fixed to the substratum by hapteroid bases. Blades are initially flabellate and later strap-like, with branches 8–15 mm broad, smooth or crenulated margins and apices bordered by zones of meristematic cells. Most fronds have microscopic veins, which become coarse and prominent in the lower thallus (Ricker, 1987).
To analyse the distribution of Antarctothoa bougainvillei on Hymenena laciniata, 21 thalli with 1,484 colonies of this bryozoan from San Sebastián Bay (Tierra del Fuego, Argentina, 53°14′–15′ S, 68°16′–17′ W) were studied under a dissecting microscope. Algae were collected at 5–13 m depth using a rectangular dredge onboard the PSV Laurel on March 11, 2006. Thalli may have been separated by hundreds of metres from one another. To estimate bryozoan and algal area, contour of each colony and thallus was traced on paper, cut-out, weighed to the nearest mg and compared with the weight of a known surface. Area of reproductive and somatic tissues of each mature thallus was estimated similarly. Error was assessed by drawing and weighing 10 times the contour of one colony. A coefficient of variation of 0.7% was obtained.
The following data were recorded for each colony: (1) side of the thallus on which it was growing, (2) area and (3) number of ovicells.
In colonies undergoing intraspecific competition (n = 223), obstructed and free-growing margins were measured using a GIS software. All intraspecific encounters were recorded, irrespective of the length of the line of contact between colonies.
In colonies where the ancestrula (Fig. 1) was still present, we measured: (1) the distance from the ancestrula to the attachment disc of the thallus (n = 874), (2) the angle between the median longitudinal axis of the ancestrula and the frond and (3) the distance from the ancestrula to the right and left edges of the thallus (n = 799). Colonies adjacent to broken algal edges were not taken into account. A colony was defined as ‘marginal’ when the distance from the ancestrula to either edge was less than 1/4 of the thallus width. The remaining colonies were regarded as ‘central’.
The null hypothesis that ancestrulae were randomly oriented with relation to the frond axis was tested by means of the Rayleigh test (Zar, 1996).
Correlation between number of ovicells and (1) colony area or (2) percentage of intraspecific contact was calculated using the Spearman non-parametric test (Sokal & Rohlf, 1981).
In mature thalli (n = 17), we measured the distance from the zone of the thallus, where tetrasporangia, cystocarps or spermatangia begin to appear, to the attachment disc. Areas and distances from all A. bougainvillei colonies to the attachment disc were taken into account to estimate the proportion of algal reproductive tissues covered by this epibiont. In colonies where the ancestrula had disappeared, its most likely location was estimated by following the direction of zooidal budding backwards in the early astogenetic zone.
Number and area of colonies were compared between both sides of the thallus by the χ2 test and one-way ANOVA, respectively, taking into account only thalli with more than five colonies on each side (n = 15). Homogeneity of variances was verified by Cochran’s C test (Winer, 1971). The relationship between number of ovicells and colony area in obstructed and free-growing colonies was analysed using ANCOVA, but the homogeneity of adjusted means could not be tested because the slopes of the regression lines were not parallel (Sokal & Rohlf, 1981).
Results
Seventeen out of 21 thalli examined in this study were mature: 11 were female, 2 were male and 4 were tetrasporangial. Algal area varied between 1.02 and 672.77 cm2 (Table 1).
The most common epibiont on Hymenena laciniata was the cheilostome Antarctothoa bougainvillei. Bivalves, ascidians, hydrozoans and the cyclostome bryozoan Bicrisia biciliata (Mac Gillivray) were extremely rare. Density of A. bougainvillei varied between 0.05 and 2.93 colonies cm−2. The smallest and largest colonies measured 0.05 and 78.74 mm2, respectively.
Percentage of the algal surface covered by A. bougainvillei (Table 1) was on average very low but extremely variable (mean: 4.43%, range: 0.02–35.76%). Percentage of algal reproductive tissues covered by this species was even lower (mean: 0.53%, range: 0–2.29%). Reproductive and somatic tissues of H. laciniata (ANOVA, F = 0.58, P = 0.45, Fig. 2A), and number of colonies of A. bougainvillei on each of these tissues (ANOVA, F = 1.64, P = 0.21, Fig. 2B) did not differ significantly. On the other hand, colonies were significantly larger on somatic than on reproductive algal tissues (logarithmic transformation, Cochran’s C = 0.62, P = 0.32; ANOVA, F = 6.64, P = 0.01, Fig. 2C).
Number of colonies was significantly higher on one side than on the other in only 1 out of 15 thalli (thallus No. 6, side A: 30, side B: 16, χ2 = 4.26, P = 0.039). Similarly, colony area was significantly larger on one side of H. laciniata than on the other in only 1 out of 15 thalli (thallus No. 7, Cochran’s C = 0.57, P = 0.138; mean: side A = 12.04 mm2, side B = 8.04 mm2; ANOVA, n = 217, F = 4.97, P = 0.027).
Central colonies were significantly more frequent than marginal ones (central: 494, marginal: 305, χ2 = 44.71, P < 1 × 10−4).
The null hypothesis that ancestrulae were randomly aligned with relation to the frond axis was rejected (Rayleigh test, z = 365.2, P < 0.001). Most ancestrulae (66.2%) faced the algal growing edge (315°–45°), showing an average angle of 0.4° (Fig. 3).
Correlation between colony area and distance from the ancestrula to the attachment disc was negative and highly significant (Spearman rank correlation, n = 874, R s = −0.287, P = 1 × 10−6), since the largest colonies predominated near the basal portions of the thalli (Fig. 4).
Percentage of colonies undergoing intraspecific competition was 15.0%. Correlation between percentage of intraspecific contact and distance from the ancestrula to the attachment disc was also negative and highly significant (Spearman rank correlation, n = 874, R s = −0.269, P < 1 × 10−6, Fig. 5A), meaning that intraspecific competition was more intense in the basal portions of the thalli.
The size frequency distribution of A. bougainvillei on H. laciniata showed that 79% of the colonies were smaller than 10 mm2 (Fig. 6). The smallest colony with ovicells measured 3.71 mm2.
Correlation between colony area and number of ovicells was highly significant (Spearman rank correlation, n = 1484, R s = 0.420, P < 0.01). Correlation between percentage of intraspecific contact and number of ovicells per unit area was positive and highly significant (Spearman rank correlation, n = 1484, R s = 0.552, P < 0.01, Fig. 5B), meaning that fecundity increases with increasing intraspecific competition. The slope of the linear regression of ovicell number on colony area was significantly higher (P < 0.0001, Fig. 7) in obstructed (y = −4.37 + 0.49x) than in free-growing (y = −0.33 + 0.12x) colonies.
Discussion
In the shallow subtidal of San Sebastián Bay, algae attached to the bottom are probably swept to and fro by strong currents filling and draining the bay with each semidiurnal tidal cycle (Isla et al., 1991). Bryozoan colonies are usually much more abundant on lower than on upper surfaces of diverse substrata to avoid sediment deposition, which is clearly harmful for most species (e.g., Lagaaij & Gautier, 1965). Colonies of Antarctothoa bougainvillei, however, showed similar densities and sizes at both sides of most thalli of Hymenena laciniata, suggesting that any of the sides of this flexible red alga would be equally suitable for the bryozoan.
Previous studies on the distribution of epiphytic bryozoans on algal surfaces showed clear spatial patterns. Colonies of Alcyonidium hirsutum (Fleming) settle preferentially along the grooves flanking the midrib of Fucus serratus L. but not on the midrib itself, and are more frequent around the midregion than on the basal and apical parts of the frond (Hayward & Harvey, 1974a). Unlike most of the brown algae whose epibiosis was analysed by previous authors, the morphology of H. laciniata is fairly simple. The main morphological features of this species are a system of microscopic veins, apical meristematic regions and reproductive organs (Mendoza, 1969; Ricker, 1987). In the present study, the higher number of colonies in central than in marginal areas could be interpreted as a larval choice to maximize future colony growth. As in other species (Stebbing, 1972; Hayward & Harvey, 1974a; Cancino, 1986), this pattern also seems to have been produced by larval behaviour, since very small colonies or even ancestrulae were well preserved throughout the thallus, implying that any post-settlement mortality of marginal colonies would have been noticed.
As the meristems of H. laciniata are apical (Mendoza, 1969; Ricker, 1987), the occurrence of large colonies near the base of the thalli was expected, since this is the oldest part of the plant. Similarly, the anascan bryozoan Jellyella (=Membranipora) tuberculata (Bosc) is also found on the basal portions of the red alga Gelidium rex Santelices et Abbott (Cancino et al., 1987; Molina et al., 1991). The opposite pattern is observed in the brown alga Laminaria, where the oldest colonies and the highest biomass of epibionts are found near the distal end of the fronds, as in this species the meristematic regions are basal (Stebbing, 1972).
The surface of H. laciniata covered by colonies of A. bougainvillei in Tierra del Fuego is relatively low. In addition, the reproductive structures of this species are mainly located in the distal portions of the thallus (Ricker, 1987), where most bryozoan colonies are younger and smaller, whereas the larger and older zoaria grow mainly over somatic tissues near the basal region of the plant. The distribution of the colonies suggests that any negative effect of this epibiont on the photosynthetic and reproductive rates of H. laciniata, if present, should be minimal.
This study shows that most ancestrulae of A. bougainvillei are oriented towards the growing edge of H. laciniata. This pattern, probably a response to unidirectional water flow (Ryland, 1974b), has already been observed in Electra pilosa (L.) on Fucus serratus and also in Jellyella tuberculata on two species of Sargassum (Ryland & Stebbing, 1971; Ryland, 1974a; reviewed in Ryland, 1974b, 1977). The orientation of ancestrulae could be interpreted as an adaptation to spreading towards younger portions of the thallus, where more substratum is available and competition for space is still less intense than in older (i.e., basal) algal surfaces.
A. bougainvillei spans a large range in latitude in Antarctica and the Subantarctic region (Hayward, 1995), showing winter pauses in feeding and growth which lead to the formation of growth check lines (Barnes & Arnold, 2001; Linse et al., 2006). In this species, growth rate increases with latitude and is inversely correlated with lifespan (Linse et al., 2006). Assuming that the Fuegian population of A. bougainvillei (53° S) grows at a similar rate (38 mm2 y−1; Linse et al., 2006) as in South Georgia (54° S), the age of 97.5% of the colonies examined in the present study can be estimated as less than 1 year. In just two colonies larger than 70 mm2 we observed only one peripheral growth check line, with further development of relatively few zooids after resuming growth, suggesting that at least a small proportion of the colonies might be slightly older than 1 year. The growth rate of this bryozoan on Fuegian H. laciniata could be higher than that estimated by Linse et al. (2006) for South Georgia, since a colony of 78.7 mm2 showed recent regrowth of relatively few zooids after its first check line.
Bryozoan lecitotrophic larvae brooded in ovicells have very short lifespans, usually settling in the vicinity of the maternal colony (e.g., Keough & Chernoff, 1987). The size frequency distribution observed in the present study, with a few large and many small colonies, suggests a massive recruitment of offspring generated by the earliest colonies, those that settled when the young thalli of H. laciniata were beginning to grow. The onset of reproduction occurs in colonies of 3.7 mm2, i.e., having an estimated age of just 1.2 months (Linse et al., 2006). This shows that A. bougainvillei, a species that loses most of its interspecific encounters against cheilostomes with spiny marginal zooids (López Gappa, 1989), assumes a strategy favouring early reproduction on ephemeral substrata, instead of allocating more resources to defend its colonies.
Algal surfaces are often the scenario where intense interspecific and interphyletic competition for space takes place (Stebbing, 1973). In the present material, however, virtually all encounters were intraspecific, due to the abundance of A. bougainvillei and the scarcity of other epibionts, and almost invariably resulted in growth arrest along the line of contact between colonies. This study shows that the rate of ovicell production of A. bougainvillei was significantly higher in colonies obstructed by conspecific neighbours than in free-growing colonies, and that the number of brood chambers per unit area increases with increasing intraspecific competition. Crowding by conspecifics also triggers the onset of sexual maturity in Membranipora spp. and Celleporella hyalina (L.) (Harvell & Grosberg, 1988; Cancino et al., 1991; Harvell & Helling, 1993). This process could well be the result of diverting energy from growth to reproduction, but experimental work has shown that colonies of C. hyalina reared with conspecific neighbours produced viable larvae, while those reared in isolation never produced female zooids (Cancino et al., 1991).
Although the present study is based on material collected at a single location, results clearly indicate that the colonies of A. bougainvillei are equally frequent on either side of most thalli, but are more frequent on central than on marginal areas, and that ancestrulae are preferentially oriented towards the younger parts of the plant. Most of the population of A. bougainvillei is composed of young colonies (<10 mm2), while larger (i.e., older) colonies are mainly found on the basal portion of the thalli, where intraspecific competition is most intense and growth obstruction by conspecific neighbours increases ovicell production. The low proportion of somatic and reproductive algal tissues covered by this bryozoan suggests that its negative effect on the alga, if any, should be minimal.
References
Barnes, D. K. A. & R. Arnold, 2001. A growth cline in encrusting benthos along a latitudinal gradient within Antarctic waters. Marine Ecology Progress Series 210: 85–91.
Buss, L. W., 1979. Habitat selection, directional growth and spatial refuges: Why colonial animals have more hiding places. In Larwood, G. P. & B. R. Rosen (eds), Biology and Systematics of Colonial Organisms. Academic Press, London: 459–497.
Cancino, J. M., 1986. Marine macroalgae as a substratum for sessile invertebrates: A study of Celleporella hyalina (Bryozoa) on fronds of Laminarina saccharina (Phaeophyta). Monografías Biológicas 4: 279–308.
Cancino, J. M., B. Casatañeda & M. C. Orellana, 1991. Reproductive strategies in bryozoans: Experimental test of the effects of conspecific neighbours. In Bigey, F. P. (ed.), Bryozoaires actuels et fossiles: Bryozoa living and fossil. Bulletin de la Société des Sciences Naturelles de l’Ouest de la France, Mémoire HS1, Nantes: 81–88.
Cancino, J. M., J. Muñoz, M. Muñoz & M. C. Orellana, 1987. Effects of the bryozoan Membranipora tuberculata (Bosc.) on the photosynthesis and growth of Gelidium rex Santelices et Abbott. Journal of Experimental Marine Biology and Ecology 113: 105–112.
Dixon, J., S. C. Schroeter & J. Kastendiek, 1981. Effects of the encrusting bryozoan, Membranipora membranacea, on the loss of blades and fronds by the giant kelp, Macrocystis pyrifera (Laminariales). Journal of Phycology 17: 341–345.
Dworjanyn, S. A., R. de Nys & P. D. Steinberg, 1999. Localisation and surface quantification of secondary metabolites in the red alga Delisea pulchra. Marine Biology 133: 727–736.
Dworjanyn, S. A., R. de Nys & P. D. Steinberg, 2006. Chemically mediated antifouling in the red alga Delisea pulchra. Marine Ecology Progress Series 318: 153–163.
Harvell, C. D. & R. K. Grosberg, 1988. The timing of sexual maturity in clonal animals. Ecology 69: 1855–1864.
Harvell, C. D. & R. Helling, 1993. Experimental induction of localized reproduction in a marine bryozoan. The Biological Bulletin 184: 286–295.
Hay, M. E., 1991. Marine–terrestrial contrasts in the ecology of plant chemical defenses against herbivores. Trends in Ecology and Evolution 6: 362–365.
Hay, M. E. & W. Fenical, 1988. Marine plant–herbivore interactions: The ecology of chemical defense. Annual Review of Ecology and Systematics 19: 111–145.
Hayward, P. J., 1973. Preliminary observations on settlement and growth in populations of Alcyonidium hirsutum (Fleming). In Larwood, G. P. (ed.), Living and fossil Bryozoa. Academic Press, London: 107–113.
Hayward P. J., 1995. Antarctic Cheilostomatous Bryozoa. Oxford University Press, Oxford.
Hayward, P. J. & P. H. Harvey, 1974a. The distribution of settled larvae of the bryozoans Alcyonidium hirsutum (Fleming) and Alcyonidium polyoum (Hassall) on Fucus serratus L. Journal of the Marine Biological Association of the United Kingdom 54: 665–676.
Hayward, P. J. & P. H. Harvey, 1974b. Growth and mortality of the bryozoan Alcyonidium hirsutum (Fleming) on Fucus serratus L. Journal of the Marine Biological Association of the United Kingdom 54: 677–684.
Hayward, P. J. & J. S. Ryland, 1975. Growth, reproduction and larval dispersal in Alcyonidium hirsutum (Fleming) and some other Bryozoa. Pubblicazioni della Stazione Zoologica di Napoli 39: 226–241.
Isla, F. I., F. E. Vilas, G. G. Bujalesky, M. Ferrero, G. Gonzalez Bonorino & A. Arche Miralles, 1991. Gravel drift and wind effects on the macrotidal San Sebastian Bay, Tierra del Fuego, Argentina. Marine Geology 97: 211–224.
Jackson, J. B. C., 1977. Competition on marine hard substrata: the adaptive significance of solitary and colonial strategies. The American Naturalist 111: 743–767.
Keough, M. J. & H. Chernoff, 1987. Dispersal and population variation in the bryozoan Bugula neritina. Ecology 68: 199–210.
Lagaaij, R. & Y. V. Gautier, 1965. Bryozoan assemblages from marine sediments of the Rhone delta, France. Micropaleontology 11: 39–58.
Linse, K., D. K. A. Barnes & P. Enderlein, 2006. Body size and growth of benthic invertebrates along an Antarctic latitudinal gradient. Deep-Sea Research II 53: 921–931.
López Gappa, J. J., 1985. Briozoos marinos de la Ría Deseado (Santa Cruz, Argentina). II. Familia Hippothoidae. Physis, Secc. A 43: 51–63.
López Gappa, J. J., 1989. Overgrowth competition in an assemblage of encrusting bryozoans settled on artificial substrata. Marine Ecology Progress Series 51: 121–130.
Manríquez, P. H. & J. M. Cancino, 1996. Bryozoan–macroalgal interactions: do epibionts benefit? Marine Ecology Progress Series 138: 189–197.
Mendoza, M. L., 1969. Las Delesseriaceae (Rhodophyta) de Puerto Deseado, Provincia de Santa Cruz, Argentina. I. Estudio sistemático y ecológico de los géneros Schizoseris Kylin, Cladodonta Skottsberg e Hymenena Greville. Physis 28: 419–441.
Mercado, J. M., R. Carmona & F. X. Niell, 1998. Bryozoans increase available CO2 for photosynthesis in Gelidium sesquipedale (Rhodophyceae). Journal of Phycology 34: 925–927.
Molina, X., J. M. Cancino & V. Montecino, 1991. Cambios en los pigmentos fotosintetizadores de Gelidium rex (Rhodophyta) inducidos por el epibionte Membranipora tuberculata (Bryozoa). Revista Chilena de Historia Natural 64: 289–297.
Moyano, H. I., 1986. Bryozoa marinos chilenos VI. Cheilostomata Hippothoidae: South Eastern Pacific species. Boletín de la Sociedad de Biología de Concepción 57: 89–135.
Muñoz, J., J. M. Cancino & M. X. Molina, 1991. Effect of encrusting bryozoans on the physiology of their algal substratum. Journal of the Marine Biological Association of the United Kingdom 71: 877–882.
Nylund, G. M. & H. Pavia, 2005. Chemical versus mechanical inhibition of fouling in the red alga Dilsea carnosa. Marine Ecology Progress Series 299: 111–121.
Ricker, R. W., 1987. Taxonomy and Biogeography of Macquarie Island Seaweeds. British Museum (Natural History), London.
Rogick, M. D. & H. Croasdale, 1949. Studies on marine Bryozoa, III. Woods Hole region Bryozoa associated with algae. The Biological Bulletin 96: 32–69.
Ryland, J. S., 1959. Experiments on the selection of algal substrates by polyzoan larvae. Journal of Experimental Biology 36: 613–631.
Ryland, J. S., 1962. The association between Polyzoa and algal substrata. Journal of Animal Ecology 31: 331–338.
Ryland, J. S., 1974a. Observations on some epibionts of gulf-weed, Sargassum natans (L.) Meyen. Journal of Experimental Marine Biology and Ecology 14: 17–25.
Ryland, J. S., 1974b. Behaviour, settlement and metamorphosis of bryozoan larvae: A review. Thalassia Jugoslavica 10: 239–262.
Ryland, J. S., 1977. Taxes and tropisms of bryozoans. In Woollacott, R. M. & R. L. Zimmer (eds), Biology of Bryozoans, Academic Press, New York: 411–436.
Ryland, J. S. & A. R. D. Stebbing, 1971. Settlement and orientated growth in epiphytic and epizoic bryozoans. In Crisp, D. J. (ed.), Proceedings of the 4th European Marine Biology Symposium. Cambridge University Press, Cambridge: 283–300.
Seed, R. & R. J. O’Connor, 1981. Community organization in marine algal epifaunas. Annual Review of Ecology and Systematics 12: 49–74.
Sokal, R. R. & F. J. Rohlf, 1981. Biometry, 2nd edn. W. H. Freeman, New York.
Stebbing, A. R. D., 1972. Preferential settlement of a bryozoan and serpulid larvae on the younger parts of Laminaria fronds. Journal of the Marine Biological Association of the United Kingdom 52: 765–772.
Stebbing, A. R. D., 1973. Competition for space between the epiphytes of Fucus serratus L. Journal of the Marine Biological Association of the United Kingdom 53: 247–261.
Wahl, M., 1989. Marine epibiosis. I. Fouling and antifouling: some basic aspects. Marine Ecology Progress Series 58: 175–189.
Winer, B. J., 1971. Statistical Principles in Experimental Design, 2nd edn. McGraw-Hill, Kogakusha.
Winston, J. E. & N. J. Eiseman, 1980. Bryozoan-algal associations in coastal and continental shelf waters of eastern Florida. Florida Scientist 43: 65–74.
Wright, P. J., P. J. Hayward & R. N. Hughes, 2007. New species of Antarctothoa (Cheilostomata: Hippothoidae) from the Falkland Isles, South Shetland Isles and the Magellan Strait. Journal of the Marine Biological Association of the United Kingdom 87: 1133–1140.
Zar, J. H., 1996. Biostatistical Analysis, 3rd edn. Prentice Hall, Upper Saddle River.
Acknowledgements
We are grateful to CONICET for financial support (PIP N° 02126), to Martín Ramírez for the SEM photograph and to Néstor Landoni and Liliana Quartino for critically reading the manuscript. Two anonymous reviewers provided valuable comments on an earlier version of this manuscript.
Author information
Authors and Affiliations
Corresponding author
Additional information
Handling editor: T. P. Crowe
Rights and permissions
About this article
Cite this article
Liuzzi, M.G., López Gappa, J. The distribution of colonies of the bryozoan Antarctothoa bougainvillei on the red alga Hymenena laciniata . Hydrobiologia 605, 65–73 (2008). https://doi.org/10.1007/s10750-008-9301-8
Received:
Revised:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s10750-008-9301-8