J. Phycol. 42, 43–50 (2006) r 2005 Phycological Society of America DOI: 10.1111/j.1529-8817.2006.00184.x ONTOGENETIC CHANGES IN BUOYANCY, BREAKING STRENGTH, EXTENSIBILITY, AND REPRODUCTIVE INVESTMENT IN A DRIFTING MACROALGA TURBINARIA ORNATA (PHAEOPHYTA)1 Hannah Louise Stewart2,3 Department of Integrative Biology, University of California, Berkeley, CA 94720-3140, USA Turbinaria ornata (Turner) J. Agardh is a tropical alga that disperses by detached, reproductively mature floating fronds. Material properties (breaking stress, breaking extension), buoyancy, and the proportion of reproductive tissue per frond were measured for juvenile, adult, and old fronds of T. ornata. Correlations between these factors indicate that as fronds age and become more reproductively mature, the tissue in their stipes (where they break) becomes weaker, more brittle, and the overall buoyancy of the frond increases. Measurement of drag force experienced by fronds from each ontogenetic stage allowed calculation of the environmental stress factor (ESF), which indicates the likelihood of detachment of a frond in the flow environment of its habitat. The ESF for fronds of each ontogenetic stage predicted that reproductively mature fronds (adult and old) break more readily than immature (juvenile) fronds. Increased proportions of reproductively mature fronds in floating rafts following storms compared with the proportion of mature fronds attached to the substratum support the ESF predictions. This combination of ontogenetic changes in material properties, buoyancy, and reproductive maturity in combination with the life history of T. ornata may contribute to the dispersal of this alga throughout French Polynesia. storms (Tunnicliffe 1981, Highsmith 1985, Bruno 1998, Boller et al. 2002), while some erect branching sponges propagate almost exclusively by asexual fragmentation (Wulff 1991). Colonies of adult ascidians have weak attachment to the surfaces, and therefore are often dislodged from the substratum, and can reattach in new areas (Worcester 1994, Edlund and Koehl 1998). Many species of marine macroalgae (Pearlmutter and Vadas 1978, Santelices and Doty 1989, Ceccherelli and Cinelli 1999, Smith and Walters 1999) and sea grass (Cambridge et al. 1983, Kuo and Kirkman 1987, Ewanchuk and Williams 1996) can also reattach after dislodgement or fragmentation, resulting in asexual dispersal. In addition to asexual propagation, drifting can also facilitate long-distance dispersal of propagules released by organisms as they drift and/or upon arrival to suitable substratum (Norton 1992). This can greatly increase the distances propagules disperse, as detached organisms that remain at the surface or in the water column can move great distances on wind and ocean currents. Dispersal distances of algal gametes, spores, and some larvae range from a few centimeters to a few meters (Dayton 1973, Paine 1979), but may reach up to several kilometers depending on currents (Reed et al. 1992, Todd et al. 1998, Gaylord et al. 2002, Shanks et al. 2003). However, rafts of buoyant seaweeds have been reported to float at the surface for up to 6 months (Helmuth et al. 1994), and can cover distances up to thousands of kilometers. For example, several species of buoyant brown algae were found to have drifted 1000 km from New Zealand to the Kermadec Islands (Nelson and Adams 1984). Durvillaea antarctica from west coast Australia has been found 5000 km from the nearest source (Kenneally 1972). French and British populations of Sargassum muticum are thought to be point sources for drift fronds found in the Dutch delta region (Critchley et al. 1987). Thus, the combination of drifting and propagule release can greatly increase the distance over which dispersal of sessile organisms can occur, relative to propagule dispersal from a sedentary organism. Whether a fragment or whole organism detaches from the substratum depends on the strength of its attachment relative to the force acting to dislodge or break it. Breaking strength, or the force required to break a structure divided by its cross-sectional area, is a function of a structure’s material properties and shape. Key index words: buoyancy; environmental stress factor; macroalga; material properties; morphology; ontogeny; Turbinaria ornata Abbreviations: ESF, environmental stress factor In the marine environment, the movement of detached whole or large pieces of sessile organisms by water motion is a common dispersal mechanism. For example, the dominant form of propagation in some reef-building corals and gorgonians is through reattachment of colony fragments broken off during 1 Received 3 February 2005. Accepted 1 October 2005. Author for correspondence: e-mail [email protected]. 3 Present address: Marine Science Institute, University of California, Santa Barbara, CA 93106-6150, USA. 2 43 44 HANNAH LOUISE STEWART Hydrodynamic forces exerted on sessile organisms in moving water are also dependent on the morphology of the organism (Denny 1988). As both breaking strength and hydrodynamic force are functions of the size and shape of an organism, ontogenetic changes in morphology can affect the potential for detachment of sessile organisms as they grow. The probability of dispersing via this mechanism may then change throughout the lifetime of the organism. Calculation of the likelihood of detachment given the morphological and biomechanical properties of the organism at a particular ontogenetic stage and the flow it encounters in its habitat at that stage (the ‘‘environmental stress factor (ESF)’’ (Johnson and Koehl 1994) enables predictions of detachment relevant to the life history and environment of the organism. Turbinaria ornata (Division Phaeophyta, Order Fucales) is a perennial macroalga common throughout volcanic islands in the South Pacific Ocean. It differs morphologically between high-flow and low-flow sites (Payri 1984, Stewart 2004). Fronds from forereef sites that experience wave-driven flow are shorter and have different morphological and material properties than fronds from calm backreef habitats dominated by relatively calm, unidirectional flow (Stewart 2004). Buoyancy is a plastic trait in response to water motion in T. ornata, with non-buoyant fronds becoming buoyant after transplantation to calm areas (H. L. Stewart, in press). Dispersal in T. ornata can operate over two spatial scales; long distance dispersal of detached buoyant fronds that drift on surface currents and small-scale dispersal of germlings released from parent fronds. Buoyant fertile floating fronds of T. ornata that detach from the substratum can form rafts that may contain thousands of thalli (C. E. Payri, personal communication) and may travel hundreds of kilometers on surface currents (Stiger and Payri 1999a, b, 2005). The abundance and distribution of T. ornata throughout French Polynesia has increased significantly since the 1980s (Payri and Stiger 2001, Stiger and Payri 2005), and dispersal by rafting of T. ornata may contribute to its success in this region (Stiger and Payri 1999a, b, Payri and Stiger 2001). To examine whether ontogenetic changes in T. ornata contribute to its potential for detachment and drifting, the properties and hydrodynamic force that contribute to the probability of detachment of T. ornata, and changes in buoyancy and reproductive maturity that contribute to the potential for rafting and fertilization success were examined to address the following questions: (1) What are the ontogenetic changes in buoyancy and reproductive investment in T. ornata? (2) How do stipe material properties and hydrodynamic force experienced by fronds of T. ornata change with ontogeny? (3) What is the predicted potential for detachment and floating of fronds at different ontogenetic stages?, and (4) How do those predictions compare with ontogenetic stages of fronds found floating on rafts in nature? MATERIALS AND METHODS Categorizing ontogenetic stages. The morphology of T. ornata varies between forereef and backreef habitats (Payri 1984, Stewart 2004). Therefore, fronds of T. ornata used in this experiment were all collected in September and October 2002 from the backreef of the barrier reef (S 171 28.699 0 W 1491 50.215 0 ) to the west of Cook’s Bay, between Tareu and Taotai passes on the island of Moorea, French Polynesia. Fronds were collected randomly from coral bommies along 30 m transects in the backreef that paralleled the reef crest. Fronds were returned immediately to the lab and held in shaded seawater tanks. Buoyancy, material properties, and reproductive investment of fronds were all quantified within 1 day of collection. To make comparisons between fronds at different ontogenetic stages, fronds of T. ornata were classified into ontogenetic groupings of juvenile, adult, and old. ‘‘Juveniles’’ were categorized as all fronds that did not yet have any reproductive receptacles. Fronds with reproductive receptacles and few epiphytes were classified as ‘‘adults’’ (Stiger and Payri 2005a). Reproductive fronds with over 50% of their surfaces covered with epibionts were considered ‘‘old.’’ This categorization follows similar distinctions for old fronds as was used by Brown et al. (1997). Ontogenetic changes in buoyancy and reproductive investment. Eight fronds of each ontogenetic stage were collected for determination of ontogenetic changes in buoyancy and reproductive investment. Net buoyant force (FB) on each algal frond was determined using the following equation: FB ¼ gVðra rw Þ ð1Þ 2 where g is the acceleration due to gravity (9.81 m/s ), V is the volume of the alga, ra is the density of the alga, and rw is the density of seawater (1023 kg/m3 at 251 C; Vogel 1994). The volume of each frond was determined to the nearest cm3 by measuring displacement of water in a graduated cylinder after a whole frond had been submerged. Fronds were then blotted dry with paper towels and the mass of each frond was determined from the mean of two measurements. Dividing the mass of each frond by its volume yielded estimates of the density of each algal frond. Reproductive investment was measured as described by Arenas and Fernandez (1998). Reproductive tissue of T. ornata is restricted to receptacles that are easily distinguishable from vegetative tissue. Fronds were quickly rinsed with fresh water to prevent salt crystals from seawater from being included in the mass measurements. All reproductive tissues were cut-off the frond, and both reproductive and vegetative tissues were dried at 601 C for at least 48 h or until its mass stopped changing in consecutive weighing. The mass of each frond and of its reproductive tissue was determined from the mean of two measurements to the nearest 0.01 g. The reproductive investment of each frond was determined by dividing the dry mass of all receptacles by the total dry frond mass (including receptacles). Material properties. To determine whether tissue material properties of T. ornata change with ontogeny, extension ratio and breaking stress of T. ornata stipes were measured by conducting tensile stress-extension tests on T. ornata stipes (as described by Koehl and Wainwright, 1977) using a tensometer constructed for field use. Measurements were made for eight fronds of each ontogenetic stage. The stipes of T. ornata were used for these tests, as this was where fronds broke when pulled experimentally from the substratum, and fronds found in floating mats were all broken along the stipe. One end of each stipe was clamped onto a stationary, machined aluminum beam. The other end of the stipe was ONTOGENETIC CHANGE IN ALGAL MORPHOLOGY clamped securely to a beam whose distance from the other beam could be altered by a hand-cranked lead screw. The original length of the portion of the stipe between the clamps was measured to the nearest 0.1 mm with digital calipers. The length of the stipe as it was pulled was measured using a linear variable differential transformer (LVDT) (Pickering & Co. Model 7308-X2-AO, Marietta, OH, USA) to the nearest 0.1 mm. The rate of extension was held constant by making one rotation of the lead screw crank each second. This produced an extension rate of 0.016/s. Voltages from the LVDT were recorded at 10 Hz and converted to digital signals using a data acquisition card (National Instruments DAQ 1200, Austin, TX, USA) and recorded on Labview software (National Instruments, Version 3.0). Voltage changes were transformed to length measurements using calibration equations established by measuring the change in voltage for a known increase in length (r2 5 0.95). The extension ratio (l) is a measure of the extension of a material, and was calculated using the following equation: l ¼ ðL Lo Þ=Lo ; ð2Þ where Lo is the original length of the stipe being tested and L is the length of the stipe as it was pulled. The force with which the stipe resisted being extended was measured by the strain gauges on the beam. Voltages generated from the deformation of the strain gauges as the stipe was pulled in tension were passed through the bridge amplifier as above. The force transducer was calibrated by hanging weights from the beam by a string to the beam at the same location as the algal stipes had been attached. The string was laid over a pulley attached to the edge of the table so that the mass of the weight caused a horizontal displacement of the beam, as occurred when the algal stipes were pulled. Weights of known masses were hung from the transducer. Each weight was hung three times and the mean of the voltages registered for each weight was multiplied by the acceleration due to gravity (9.81 m/s2) to yield the force applied to the beam. A linear regression (r2 5 0.86) was calculated for the relationship between voltage and force, with a precision of 0.001 N. The breaking stress (sBRK) is the stress at which the specimen broke and is a measure of the strength of the tissue. The breaking stress (s) for each stipe as it was pulled was calculated by s ¼ F=A; ð3Þ where F is the force required to break the specimen and A is the cross-sectional area of the stipe at the point at which it broke. The diameter of each stipe was measured using callipers with a precision of 0.1 mm, and the area calculated using the equation for the area of a circle, as stipes were roughly circular in cross section. Predicting the potential for detachment—drag force and ESF. The potential for detachment of a frond depends on the force it experiences in moving water and its ability to contend with that force. Because backreef fronds of T. ornata are exposed primarily to unidirectional water flow, drag force is the predominant hydrodynamic force acting on fronds as they are pulled in tension by water moving around them. Calculation of the drag force and the material properties of the stipe (measured above) allowed estimation of the ESF, a measure of the likelihood of detachment of fronds in the backreef. Drag. It was not possible to measure drag on the same individuals that were used in the material properties experiments, because in those experiments fronds were used immediately upon collection and broken in the course of measuring their breaking strength and extensions. Therefore, the drag force that these fronds likely would have ex- 45 perienced at a range of unidirectional flow velocities was estimated as follows. Drag force (Fd) on macroscopic objects in moving water is given by Fd ¼ 12rU2 SCd ð4Þ where r is the density of water, U is the velocity of the water past the body, S is the plan area of the object, and Cd is the drag coefficient, a function of the shape of the object. As S and Cd are properties of the individual fronds, these parameters were estimated for backreef fronds of the same length as those used in the material properties experiments. The planar area (S) of fronds of the lengths used in the material properties experiment was approximated from a correlation established between length and planar area (r2 5 0.65) of 10 randomly collected backreef fronds. Both parameters were determined from the mean of two measurements of digital photos using NIH image software (version 1.61, National Institute of Health, Bethesda, MD, USA). Drag measurements were conducted in a flow tank at the University of California at Berkeley using fronds that had been transported from Moorea. Fronds were collected wrapped in wet paper towel and enclosed in an airtight plastic bag for 12 h during air transport from Moorea to Berkeley, where they were held in an aerated saltwater aquarium. Fronds were used in the drag experiments up to 3 days after collection, and damage or disintegration of tissue was not evident at that time. Drag measurements were conducted in a flow tank with a working section of 0.35 0.50 2.00 m. Water velocity in the tank was measured at average mid-frond height of adults (8.0 cm) with an acoustic Doppler anemometer (SonTek Inc., San Diego, CA, USA) to the nearest 0.001 m/s. Drag on each frond was measured with force transducers (Koehl 1977). Fronds were attached at the base of their stipes with a cable tied to the sting of a force transducer that poked up through a false bottom on the floor of the flow tank. The force signal was passed from the transducer through the bridge amplifier to the DAQ card recorded on Biobench software (National Instruments, Austin, TX, USA) on a laptop computer. Voltages from the force transducer were recorded at 10 Hz and averaged over 30 s intervals. The force transducer used in the drag experiments was calibrated in the same manner as that used in the material properties tests described above. A linear regression (r2 5 0.88) was calculated to describe the relationship between voltage and force, with a precision of 0.001 N. The drag coefficient (Cd) was estimated to be the mean of the drag coefficients measured for ten adult backreef fronds at a range of flow speeds from 0.16 to 0.73 cm/s in a unidirectional flow tank. The drag force that would likely have been experienced by the fronds of the lengths used in the material properties tests was then calculated using the Cd and the S estimated as above. As the Cd did not change significantly between flow speeds, the Cd at the highest flow speed (0.73 m/s) was used in drag calculations to extrapolate to drag forces at flow speeds faster than those possible in the flume. This may have overestimated drag at higher flow speeds as Cd can decrease as flow speeds decrease (Carrington 1990). Drag was estimated at flow speeds from 0.73–3.5 m/s, a range of flow speeds that spans estimates of instantaneous maximum flow speed in the backreef (1.0–1.25 m/s J. Hench, personal communication). The mean values of drag of the 10 measurements for each ontogenetic stage at the highest flow speed in the flume (0.73 m/s) were compared using a one-way ANOVA and a Tukey–Kramer multiple comparison in Matlab (version 7.01, Mathworks Inc., Natick, MA, USA). ESF. The ESF is a measure of the resistance to detachment or breakage of an organism at a particular time in its 46 HANNAH LOUISE STEWART beginning with 12:00 p.m. in the North direction. All transects passed through the center of the raft. A total of 179 fronds were collected from four rafts. Ontogenetic stage and length of attached fronds were determined by collecting all fronds within 10 cm on one side of three 10 m transect tapes placed randomly within the backreef. The ontogenetic stage was determined as above. A total of 214 fronds were collected from the three transects. 0.3 0.25 0.08 0.06 0.15 0.1 0.05 0.04 0.02 0 –0.02 0 r 2=0.81 p<0.05 0 5 10 15 20 25 Length (cm) 30 35 10 8 6 4 2 r 2=0.48 0 0 5 10 15 20 25 Length (cm) r 2=0.78 p<0.05 – 0.04 D 1.5 Breaking extension ratio Breaking stress (MN . m–2) B 0.2 –0.05 C RESULTS Ontogenetic changes in buoyancy and reproductive investment. Net buoyant force of fronds of T. ornata increased with frond length and advanced ontogenetic stage (Figs. 1 and 2). This appears to be due to the increased relative volume of pneumatocysts inside blades at the distal portion of fronds relative to blades proximal to the holdfast. The reproductive receptacles of T. ornata are independent ancillary structures (Fig. 3), and the proportion of frond dry mass made up of reproductive tissue increased with frond length and with advanced ontogenetic stage (Fig. 1). Reproductive tissue made up 20% of total biomass in adult fronds and up to 25% in old fronds (Fig. 2). Net buoyant force experienced by fronds of T. ornata increased with proportion of mass made up of reproductive tissue (Fig. 2). Net buoyant force (N) A Proportion mass reproductive ontogeny, relative to the peak forces it experiences in its habitat at that time (Johnson and Koehl 1994). The ESF is calculated from the ratio of the breaking stress of the stipe at a particular stage in its ontogeny (calculated above) divided by the stress owing to drag experienced by the frond in flow velocities experienced during that season in its habitat. For backreef fronds of T. ornata, the ESF was calculated as the ratio of the breaking stress of the stipe (calculated above) divided by the estimated stress owing to drag experienced by each frond. Stress in the stipe owing to drag was calculated by dividing drag force by the cross-sectional area of the stipe of a frond of a particular length used in the material properties tests. An estimate of the ESF was calculated for ten fronds of each ontogenetic group (juvenile, adult, and old) for flow speeds from 0.16 to 3.5 m/s. An ESF of greater than 1 suggests that the organism will not detach from the substratum and an ESF of less than 1 predicts that the organism will break. Ontogenetic stages of fronds floating in mats and attached to the substratum. To compare predictions of detachment of T. ornata based on the calculated ESFs for each ontogenetic stage to what was found in the field, the ontogenetic stage and length of fronds attached to the substratum and floating in rafts in a backreef were determined. Detached, floating fronds were collected using random transects through four floating rafts of T. ornata. Transects were conducted by driving a small skiff slowly through a raft and collecting all fronds within 1 m on one side of the boat. The orientation of transects through the raft was determined using a random number table to select a starting position around the edge of the raft. Numbers from 1 to 12 were assigned like a clock 1.4 0 35 10 15 20 25 Length (cm) 30 35 30 35 1.3 1.2 1.1 r 2=0.68 p<0.05 p<0.05 30 5 1 0 5 10 15 20 25 Length (cm) FIG. 1. Correlations between length (cm) and frond characteristics for juvenile ( ), adult (&), and old (4) fronds. (A) Proportion of total frond dry mass made up of reproductive material, plotted as a function of frond length. (B) Net buoyant force (N) of fronds plotted as a function of length. (C) Breaking stress (N/m2) plotted as a function of length of stipes pulled in tension. (D) Breaking extension ratio as a function of length of stipes pulled in tension. ONTOGENETIC CHANGE IN ALGAL MORPHOLOGY A 0.08 47 r 2=0.61 p<0.05 Net buoyant force (N) 0.06 0.04 0.02 0 –0.02 B 10 Breaking stress (MN . m–2) –0.04 –0.05 8 Breaking extension ratio 0.05 0.1 0.15 0.2 0.25 Proportion mass reproductive 0.3 r 2=0.46 p<0.05 6 4 FIG. 3. Photograph of a blade of Turbinaria ornata with reproductive receptacle. 2 0 –0.05 C 0 0 1.5 0.05 0.1 0.15 0.2 0.25 Proportion mass reproductive 0.3 r 2=0.57 p<0.05 1.4 1.3 1.2 1.1 1 –0.05 0 0.05 0.1 0.15 0.2 0.25 Proportion mass reproductive 0.3 FIG. 2. (A) Net buoyant force (N). (B) Breaking stress (MN/ m2). (C) Breaking extension ratio, plotted as functions of the proportion of mass made up of reproductive material for juvenile ( ), adult (&), and old (4) fronds. Material properties. Breaking stress and breaking extension ratio of stipes of T. ornata decreased with frond length and advanced ontogenetic stage (Fig. 1), and with reproductive investment (Fig. 2). Potential for detachment—drag and ESF. Drag force increased with flow velocity from 0.16 to 3.5 m/s and was higher for old and adult fronds than juvenile fronds at all flow speeds (Fig. 4). These values likely overestimate drag at high flow speeds, as the value for Cd at the highest flow speed possible in the flume (73 cm/s) was used to calculate drag forces at flow speeds faster than those possible in the flume. In general, Cd for algae is expected to decrease with increasing flow speed as algae are reconfigured into increasingly streamlined shapes as flow gets faster (Carrington 1990). At the highest flow speeds generated by the flume used in this experiment, there was no evidence of decreasing Cd, although it is likely that Cd would have decreased at higher flow speed. However, the unique pinecone-like shape of T. ornata does not streamline like other foliose algae, and so the extent to which the Cd may have decreased is difficult to estimate. A decrease in the coefficient of drag would tend to increase the ESF for all stages, but not likely change the relative ESF of the different stages. Calculations of the ESF for all ontogenetic stages showed that ESF decreased with increasing flow speeds from 0.16 to 3.5 m/s, and that ESF was higher for juveniles than for adults and old fronds (Fig. 4). Thus, mature (adult and old) fronds should detach from the substratum more readily than juvenile fronds. Ontogenetic stage of fronds attached to the substratum and floating in mats. Of fronds that were attached to the substratum, 70% were juveniles, 26% were adults, and 5% were old (Fig. 5). However, only one of the 179 fronds collected from the floating rafts was a juvenile, whereas 21% were adults and 79% were old (Fig. 5). 48 A HANNAH LOUISE STEWART 1 juvenile adult old Drag (N) 0.8 0.6 0.4 0.2 0 0 0.1 0.2 0.3 0.4 0.5 Flow speed (m . s–1) 0.6 0.7 0.8 Environmental stress factor B 100 juvenile adult old 10 1 0 1 2 3 4 5 0.1 Flow speed (m . s–1) FIG. 4. (A) Drag force (N) measured at unidirectional flow velocities from 0.16 to 0.73 m/s in a flow tank for juvenile ( ), adult (&), and old (4) fronds (mean SE, n 5 10). Means at the highest flow speed are significantly different from one another as determined by a one-way ANOVA (f 5 163.52, df 5 2, Po0.05) and Tukey–Kramer multiple comparisons. (B) Estimated mean environmental stress factors (ESFs) at unidirectional flow velocities from 0.16 to 3.5 m/s for juvenile ( ), adult (&), and old (4) fronds (mean SE, n 5 10). As the ESF approaches 1, the potential for breakage increases. DISCUSSION The correlations between increasing buoyancy and reproductive maturity, and decreasing tissue strength and extensibility with increasing ontogenetic stage noted in this study indicate a potentially important mechanism by which morphological ontogenetic changes may contribute to the dispersal abilities of T. ornata. The negative correlations between stipe breaking strength and extensibility with ontogeny indicate that, as fronds mature, their stipes become weaker and less extensible. Older fronds are also longer and experience greater drag force than younger, shorter fronds. Taken together, this increases the chance that older A B juvenile adult old FIG. 5. Proportion of juvenile, adult, and old fronds (A) attached to the substratum and (B) in floating rafts of Turbinaria ornata in the backreef in Moorea in November 2003. fronds, which are more reproductively mature and buoyant, are more likely to detach as flow speeds increase, than are juveniles, as predicted by ESF. Indeed, floating rafts of T. ornata are composed primarily of mature fronds, with very few juveniles, supporting predictions based on ESF. This is in striking contrast to the proportions of juvenile, adult, and old fronds in attached populations of T. ornata, in which juveniles form the majority. The positive correlation between reproductive capacity and buoyancy ensures that detached fertile floating fronds have the potential for sexual reproduction in these mats. A survey of the ontogenetic stages of fronds in mats in this study indicates that the vast majority (99%) of T. ornata fronds in mats are reproductively mature. Ova in female fronds are fertilized by male gametes that are released in response to phases of the moon (Stiger 1997), and fertilization success may be enhanced for detached fronds that have been blown together at the time of gamete release. Because release of male gamete of T. ornata may take place in mats of fronds, eggs from female fronds may be fertilized by gamete from different male fronds, and it is conceivable that the population resulting from the zygotes of a single female frond may be genetically diverse. Each female frond of T. ornata can produce hundreds of eggs, which only disperse up to 0.9 m from the parent frond when released (Stiger and Payri 1999 b). In contrast to kelps, Fucales do not alternate sporophyte and gametophyte generations. The gametophyte is reduced to eggs and sperm. Eggs are fertilized in and retained within the receptacle of the female sporpphyte, and zygotes released from the female develop directly into sporophyte fronds without intermediary development of gametophyte fronds. They are therefore freed from the proximity and density settlement requirements for female and male gametophytes that can limit fertilization in kelps (North 1971). Therefore, an individual fertilized female frond has the ability to produce a genetically diverse population in a new area. The life history of T. ornata combines aspects of strategies that include fast-growing, short-lived weedy species composed of weak thalli that produce spores soon after settling and are easily broken by seasonal storms, and strong, slow-growing space-holders that are slow to produce spores and can grow back from their holdfasts if broken off (Koehl 1984, 1999, Santelices and Varela 1994, Pratt and Johnson 2002). Holdfasts of T. ornata are perennial, but thalli frequently break off from the holdfast during storms, leaving the holdfast intact and attached to the substratum (H. L. Stewart, unpublished data). Removal of the main stipe of T. ornata results in the growth of one of the small ‘‘ladies in waiting’’ fronds that are present in diminutive form at the base of the primary stipe on the holdfast (H. L. Stewart and C. E. Payri, unpublished data). Therefore, a stipe of a mature individual that is detached from its holdfast is replaced by a frond of the same genetic individual, while at the same time dispersing zygotes to new locations on reproductively ONTOGENETIC CHANGE IN ALGAL MORPHOLOGY mature fronds via rafting. This conveyor belt-like supply of reproductively mature fronds from individual holdfasts likely contributes to the success of T. ornata. The mean positive buoyant force experienced by adult fronds (0.023 0.006 N) is small relative to hydrodynamic forces exerted on fronds in the backreef on a relatively calm day ( 0.4 N) (Stewart 2004). However, this buoyant force contributes a tensile force to the overall forces acting on the stipe. Perhaps more importantly, the buoyancy of a detached frond maintains its position at the water’s surface, where it is subject to wind-driven surface currents. Currents and wind congregate detached fronds from different locations into large mats, and fertilization in these mats may help maintain genetic connectivity between populations, as mentioned above. Buoyancy also keeps detached fronds near the surface where light is abundant for photosynthesis and may contribute to the long (3 month) period that T. ornata can stay alive and not disintegrate while floating (C. E. Payri, personal communication). The factors affecting whether or not an alga will detach from the substratum are varied (e.g. hydrodynamic regime, morphology, and ontogeny). Similarsized algae in the same habitat may have very different ESFs, as was found for two intertidal seaweed species Chondrus crispus and Mastocarpus stellatus, where differences in stipe cross-sectional area lead to different patterns of dislodgment in the same habitat (Dudgeon and Johnson 1992, Pratt and Johnson 2002). The ESF for an organism may also vary between season, site, and life history stage. Changes to morphology that affect hydrodynamic forces and changes in tissue strength can change the ESF an organism experiences. Such changes may occur in response to different stages in an organism’s life cycle, as found in this study, and in habitats experiencing different flow conditions (Johnson and Koehl 1994, Pratt and Johnson 2002). The combination of the life history of T. ornata, the correlations between ontogenetic changes in material properties, buoyancy, and reproductive investment is well suited for the success of this species in the smattering of islands in the South Pacific. Islands range in distance from one another from hundreds to thousands of kilometers, and floating mats of T. ornata may drift between islands, establishing populations in new locations and dispersing to adjacent islands (as suggested by Stiger and Payri (1999 b). Indeed the distribution and abundance of T. ornata throughout French Polynesia has increased dramatically since the 1980s (Payri and Stiger 2001, Stiger and Payri 2005) and T. ornata is now common in areas where it had previously not been recorded. SUMMARY The results of this study indicate that during ontogeny, fronds of T. ornata experience an increase in the proportion of tissue made up of reproductive tissue, an increase in buoyancy, and a decrease in tissue breaking 49 strength and extensibility. Thus, as fronds age and become reproductively mature, their stipes become weaker and the buoyant forces they experience increase. In addition, fronds increase in size as they age, increasing the hydrodynamic drag experienced by older algae in moving water. Thus older, fertile fronds face increasing risk of detachment from the substratum, and increased likelihood that detached fronds will float. The ESFs of juvenile, adult, and old fronds indicate that the likelihood of detachment of adult or old fronds (both of which are reproductively mature) is greater than that of a juvenile at all flow speeds from 1 to 5 m/s. This prediction is supported by the pattern of ontogenetic stages of fronds randomly collected from four floating rafts of fronds in the backreef, the majority of which were fertile. These ontogenetic changes to buoyancy, tissue strength, and reproductive capacity in combination with the life history of T. ornata likely play a role in the success of this alga. Thanks to M. Koehl, T. Dawson, and M. Stacey for advice and guidance throughout this project. Special thanks to C. Payri for sharing her expertise on the natural history of T. ornata, and to Ann Stewart, Jacques Yoo-Sing, and Tony Yoo-Sing for help in the field. Comments from D. Reed and two anonymous reviewers improved the quality of this manuscript. This research was funded by a graduate fellowship from the Natural Science and Engineering Research Council (NSERC) of Canada, a PEARL graduate fellowship from the University of California at Berkeley Richard R. Gump South Pacific Research Station, and a Ralph I. Smith Fellowship to H. L. Stewart. Additional funding was provided by National Science Foundation grants #OCE9907120 and #OCE-0241447 to M. Koehl and the Moorea Coral Reef LTER. This is contribution #133 of UC Berkeley’s Richard B. Gump South Pacific Research Station, Moorea, French Polynesia. Arenas, F. & Fernandez, C. 1998. Ecology of Sargassum muticum (Phaeophyta) on the North coast of Spain – III. Reproductive ecology. Bot. Marina 41:209–16. Boller, M. L., Swain, T. D. & Lasker, H. R. 2002. Skeletal morphology and material properties of a fragmenting gorgonian coral. Marine Ecol. Progr. Ser. 228:131–41. Brown, M. T., Nyman, M. A., Keogh, J. A. & Chin, N. K. M. 1997. Seasonal growth of the giant kelp Macrocystis pyrifera in New Zealand. Marine Biol. 129:417–24. Bruno, J. F. 1998. Fragmentation in Madracis mirabilis (Duchassaing and Michelotti): how common is size-specific fragment survivorship in corals? J. Exp. Marine Biol. Ecol. 230:169–81. Cambridge, M. L., Carstairs, S. A. & Kuo, J. 1983. An unusual method of vegetative propagation in Australian Zosteraceae. Aquatic Bot. 15:201–4. Carrington, E. 1990. Drag and dislodgment of an intertidal macroalga: consequences of morphological variation in Mastocarpus papillatus Kutzing. J. Exp. Marine Biol. Ecol. 139:185–200. Ceccherelli, G. & Cinelli, F. 1999. The role of vegetative fragmentation in dispersal of the invasive alga Caulerpa taxifolia in the Mediterranean. Marine Ecol.-Progr. Ser. 182: 299–303. Critchley, A. T., Neinhuis, P. H. & Verschuure, K. 1987. Presence and development of populations of the introduced brown alga Sargassum muticum in Southewest Netherlands. Hydrobiologia 151–152:245–55. Dayton, P. K. 1973. Dispersion dispersal and persistence of the annual Inter tidal alga Postelsia-palmaeformis. Ecology 54:433–8. Denny, M. W. 1988. Biology and the Mechanics of the Wave-Swept Environment. Princeton University Press, Princeton, NJ. 50 HANNAH LOUISE STEWART Dudgeon, S. R. & Johnson, A. S. 1992. Thick vs. thin Thallus morphology and tissue mechanics influence differential drag and dislodgement of two co-dominant seaweeds. J. Exp. Marine Biol. Ecol. 165:23–43. Edlund, A. F. & Koehl, M. A. R. 1998. Adhesion and reattachment of compound ascidians to various substrata: weak glue can prevent tissue damage. J. Exp. Biol. 201:2397–402. Ewanchuk, P. J. & Williams, S. L. 1996. Survival and re-establishment of vegetative fragments of eelgrass (Zostera marina). Can. J. Bot. 74:1584–90. Gaylord, B., Reed, D. C., Raimondi, P. T., Washburn, L. & McLean, S. R. 2002. A physically based model of macroalgal spore dispersal in the wave and current-dominated nearshore. Ecology 83:1239–51. Helmuth, B., Veit, R. R. & Holberton, R. 1994. Long-distance dispersal of a subantarctic brooding bivalve (Gaimardia trapesina) by kelp-rafting. Marine Biol. 120:421–6. Highsmith, R. C. 1985. Floating and algal rafting as potential dispersal mechanisms in brooding invertebrates. Marine Ecol. Progr. Ser. 25:169–79. Johnson, A. S. & Koehl, M. A. R. 1994. Maintenance of dynamic strain similarity and environmental- stress factor in different flow habitats – thallus allometry and material properties of a giant-kelp. J. Exp. Biol. 195:381–410. Kenneally, K. F. 1972. Tropical seeds and fruit washed up on the south-west coast of Western Australia. Western Aust. Nat. 12: 73–80. Koehl, M. A. R. 1977. Effects of sea anemones on the flow forces they encounter. J. Exp. Biol. 69:87–105. Koehl, M. A. R. 1984. How do benthic organisms withstand moving water? Am. Zool. 24:57–70. Koehl, M. A. R. 1999. Ecological biomechanics: life history, mechanical design, and temporal patterns of mechanical stress. J. Exp. Biol. 202:3469–76. Koehl, M. A. R. & Wainwright, S. A. 1977. Mechanical adaptations in a giant kelp. Limnol. Oceanogr. 22:1067–71. Kuo, J. & Kirkman, H. 1987. Floral and seedling morphology and anatomy of Thalassodendron-Pachyrhizum Den Hartog Cymodoceaceae. Aquatic Bot. 29:1–18. Nelson, W. A. & Adams, N. M. 1984. Marine algae of the Kermadec Islands. National Museum of N. Z. Misc. Ser., pp. 29. North, W. J. 1971. The biology of giant kelps beds (Macrocystis) in California. Nova Hedw. Beih. 32:1–98. Norton, T. A. 1992. Dispersal by macroalgae. Br. Phycol. J. 27: 293–301. Paine, R. T. 1979. Disaster, catastrophe and local persistence of the sea-palm Postelsia palmaeformis. Science (Washington DC) 205:685–7. Payri, C. E. 1984. Variations biologiques et morphologiques en fonction du milieu chez Turbinaria ornata (Turner) J. Agardh (Pheophycees) du recif de Tiahura- Ile de Moorea- Polynesie Francaise. Bot. Marina 17:327–33. Payri, C. E. & Stiger, V. 2001. Macroalgal community changes on French Polynesian reefs, 1980–2000. Phycologia 40:111. Pearlmutter, N. L. & Vadas, R. L. 1978. Regeneration of thallus fragments of Rhodochorton purpureum (Rhodophyta, Nemalionales). Phycologia 17:186–90. Pratt, M. C. & Johnson, A. S. 2002. Strength, drag, and dislodgment of two competing intertidal algae from two wave exposures and four seasons. J. Exp. Marine Biol. Ecol. 272:71–101. Reed, D. C., Amsler, C. D. & Ebeling, A. W. 1992. Dispersal in kelps: factors affecting spore swimming and competency. Ecology 73:1577–85. Santelices, B. & Doty, M. S. 1989. A review of Gracilaria farming. Aquaculture 78:95–133. Santelices, B. & Varela, D. 1994. Abiotic control of reattachment in Gelidium chilense (Montagne) Santelices and Montalva (Gelidiales; Rhodophyta). J. Exp. Marine Biol. Ecol. 177:145–55. Shanks, A. L., Grantham, B. A. & Carr, M. H. 2003. Propagule dispersal distance and the size and spacing of marine reserves. Ecol. Appl. 13:S159–69. Smith, C. M. & Walters, L. J. 1999. Fragmentation as a strategy for Caulerpa species: fates of fragments and implications for management of an invasive weed. Marine Ecol. 20:307–19. Stewart, H. L. 2004. Hydrodynamic consequences of maintaining an upright posture by different magnitudes of stiffness and buoyancy in the tropical alga Turbinaria ornata. J. Marine Syst. 49:157–67. Stewart, H. L. Morphological variation and phenotypic plasticity of buoyancy in the macroalga Turbinaria ornata across a barrier reef. Marine Biology (in press). Stiger, V. 1997. Contribution a l’etude de la biologie des populations de deux grandes algues brunes Turbinaria ornata (Turner) J. Agardh et Sargassum mangarevense (Grunow) Setchell, proliferant sur les recifs de Polynesie francaise. Universite Francaise du Pacifique. Stiger, V. & Payri, C. E. 1999a. Spatial and seasonal variations in the biological characteristics of two invasive brown algae, Turbinaria ornata (Turner) J. Agardh and Sargassum mangarevense (Grunow) Setchell (Sargassaceae, Fucales) spreading on the reefs of Tahiti (French Polynesia). Bot. Marina 42: 295–306. Stiger, V. & Payri, C. E. 1999b. Spatial and temporal patterns of settlement of the brown macroalgae Turbinaria ornata and Sargassum mangarevense in a coral reef on Tahiti. Marine Ecol. Progr. Ser. 191:91–100. Stiger, V. & Payri, C. E. 2005. Natural settlement dynamics of a young population of Turbinaria ornata and phenological comparisons with older populations. Aquatic Bot. 81:225–43. Stewart, H. L. Morphological variation and phenotypic plasticity of buoyancy in the macroalga Turbinaria ornata across a barrier reef. Marine Biology (in press). Todd, C. D., Lambert W. J. & Thorpe, J. P. 1998. The genetic structure of intertidal populations of two species of nudibranch molluscs with planktotrophic and pelagic lecithotrophic larval stages: are pelagic larvae ‘‘for’’ dispersal? J. Exp. Marine Biol. Ecol. 229:1–28. Tunnicliffe, V. 1981. Breakage and propagation of the stony coral Acropora cervicornis. Proc. Natl. Acad. Sci. USA 78:2427–31. Vogel, S. 1994. Life in Moving Fluids—The Physical Biology of Flow. 2nd ed. Princeton University Press, Princeton, NJ. Worcester, S. E. 1994. Adult rafting versus larval swimming: dispersal and recruitment of a botryllid ascidian on eelgrass. Marine Biol. 121:309–17. Wulff, J. L. 1991. A sexual fragmentation genotype success and population dynamics of erect branching sponges. J. Exp. Marine Biol. Ecol. 149:227–48.
© Copyright 2026 Paperzz