MEC_1448.fm Page 329 Wednesday, February 20, 2002 9:07 AM Molecular Ecology (2002) 11, 329 – 345 The contribution of haploids, diploids and clones to fine-scale population structure in the seaweed Cladophoropsis membranacea (Chlorophyta) Blackwell Science Ltd H . J . V A N D E R S T R A T E , * † L . V A N D E Z A N D E , † W . T . S T A M and J . L . O L S E N * *Department of Marine Biology, Centre for Ecological and Evolutionary Studies, University of Groningen, PO Box 14, 9750 AA Haren, The Netherlands, †Department of Population Genetics, Centre for Ecological and Evolutionary Studies, University of Groningen, PO Box 14, 9750 AA Haren, The Netherlands Abstract Local populations of Cladophoropsis membranacea exist as mats of coalesced thalli composed of free-living haploid and diploid plants including clonally reproduced plants of either phase. None of the phases are morphologically distinguishable. We used eight microsatellite loci to explore clonality and fine-scale patch structure in C. membranacea at six sites on the Canary Islands. Mats were always composites of many individuals; not single, large clones. Haploids outnumbered diploids at all sites (from 2:1 to 10:1). In both haploid and diploid plants, genetic diversity was high and there was no significant difference in allele frequencies. Significant heterozygote deficiencies were found in the diploid plants at five out of six sites and linkage disequilibrium was associated with the haploid phase at all sites. Short dispersal distances of gametes/spores and small effective population sizes associated with clonality probably contribute to inbreeding. Spatial autocorrelation analysis revealed that most clones were found within a radius of ≈ 60 cm and rarely further than 5 m. Dominance of the haploid phase may reflect seasonal shifts in the relative frequencies of haploids and diploids, but may alternatively reflect superiority of locally adapted and competitively dominant, haploid clones; a strategy that is theoretically favoured in disturbed environments. Although sexual reproduction may be infrequent in C. membranacea, it is sufficient to maintain both life history phases and supports theoretical modelling studies that show that haploid–diploid life histories are an evolutionarily stable strategy. Keywords: alga, clonality, dispersal, isomorphic diplohaplontic life history, microsatellites, population genetic structure Received 2 August 2001; revision received 15 November 2001; accepted 15 November 2001 Introduction Population structure is the complex result of many interacting genetic and demographic factors set against a dynamic environmental background. A description of spatial genetic structure at different scales provides a way to examine the processes that have affected the evolution and ecology of species. One of these processes is dispersal, the amount of which is directly related to the reproductive system (Loveless & Hamrick 1984). Studies in terrestrial plants (mainly Correspondence: Han van der Strate. Present address: †Department of Marine Biology, Centre for Ecological and Evolutionary Studies, University of Groningen, PO Box 14, 9750 AA Haren, The Netherlands. Fax: + 31– 50 – 3632261; E-mail: [email protected] © 2002 Blackwell Science Ltd angiosperms) show that mating systems and dispersal capabilities are excellent predictors of genetic diversity, structure and gene flow over a range of spatial scales (Hamrick et al. 1979; Loveless & Hamrick 1984; Schoen & Brown 1991). Marine plants, including seaweeds, exhibit an extremely diverse range of life histories (Van den Hoek et al. 1995) which offer a unique opportunity to investigate the relationship between life history strategies and dispersal capacity in the aquatic realm. The seaweed Cladophoropsis membranacea (Hofman Bang ex. C. Agardh) Børgesen grows on rocky benches and reefs in wave-swept or high-surge, intertidal zones in the tropics and subtropics. In the Canary Islands it grows on basalt benches (50–500 m wide). Thalli consist of intertwined, loosely branched, filaments. The multinucleate construction MEC_1448.fm Page 330 Wednesday, February 20, 2002 9:07 AM 330 H . J . V A N D E R S T R A T E E T A L . Fig. 1 Haplodiplo-isomorphic life history of Cladophoropsis membranacea. It is not known whether gametophytes are dioecious or monoecious. Asexual reproduction via gametes and/or mitospores has been reported for both generational phases. and paucity of cross-walls gives rise to the distinctive siphonous morphology. Thalli form dense cushions and mats 1–2 cm thick that may extend > 50 cm. C. membranacea is most abundant from the autumn to late spring. In some habitats it can become transiently dominant. The life history of Cladophoropsis (SiphonocladalesCladophorales Complex, Ulvophyceae) is characterized by a diplohaplontic–isomorphic alternation of generations (Van den Hoek et al. 1995). As illustrated in Fig. 1, populations consist of independent, free-living haploid and diploid phases that are morphologically indistinguishable. In addition, asexual reproduction (Bodenbender et al. 1988; Bodenbender & Schnetter 1990; Kapraun & Nguyen 1994) via parthenogenesis of gametes and/or the production of mitospores in one or both phases, may add clonal structure to the population. It is not known whether the haploid or diploid phases of the life history sequentially dominate or coexist throughout the year, nor is it known to what extent asexual reproduction augments one or both phases. Over the past 20 years many efforts have been made to gain a better understanding of direct dispersal (reviewed by Norton 1992b) and population genetic structure in algae using isozyme electrophoresis (reviewed by Sosa & Lindstrom 1999) as an indirect measurement of gene flow. Low levels of allozyme variation have often limited the power of these studies and led to the questionable conclusion of extremely broad-scale panmixis. However, a handful of studies have shown population differentiation at scales of tens to hundreds of kilometres, that roughly matched predictions related to dispersal capability and the mating system. In seaweeds, dioecy and outcrossing have been investigated by Lu & Williams (1994) in Halidrys, by Benzie et al. (1997) in Caulerpa, and by Hwang et al. (1998) in Porphyra. Monoecy and selfing have been investigated by Williams & Di Fiori (1996) in Pelvetia; and asexuality by Innes (1988) in Enteromorpha and Ulva, by Intasuwan et al. (1993) in Gracilaria, by Pearson & Murray (1997) in Lithothrix, by Sosa et al. (1996) in Gracilaria and by Sosa et al. (1998) in Gelidium. Evidence for short-distance dispersal at a scale of metres has come mainly from direct measurements of settling or spore filtration studies [reviewed in Destombe et al. 1990, 1992; Norton 1992a,b; (Gracilaria); Berndt & Brawley 2000 (Fucus)]. These studies report distances ranging from 1 to 20 m for most species. Indirect measurements using highresolution, genetic markers (such as fingerprinting and microsatellite loci), at very small scales, are still in the early stages. Coyer et al. (1997) investigated dispersal within clusters of Postelsia to be limited to < 5 m; Engel et al. (1999) examined paternity relationships in Gracilaria and found 80% of the mate pairs within 85 cm; and Wright et al. (2000) examined patch structure in Delisea and found differences at scales between 50 and 300 cm. The contribution of clonal reproduction has been investigated in only a few cases. Cheney & Babbel (1978) found new recruits of Eucheuma near the parent plants; Innes & Yarish (1984) observed only 13 out of a possible 5400 multilocus phenotypes in more than 1000 individuals of Enteromorpha linza; Sosa et al. (1996) found almost no variation in Gracilaria cervicornis populations; and Sosa et al. (1998) found significant differences in allele frequencies between the haploid and diploid phases in Gelidium © 2002 Blackwell Science Ltd, Molecular Ecology, 11, 329 – 345 MEC_1448.fm Page 331 Wednesday, February 20, 2002 9:07 AM P O P U L A T I O N S T R U C T U R E O F C L A D O P H O R O P S I S M E M B R A N A C E A 331 arbuscula with strong differentiation in the haploid, asexual phase. In this study we used recently developed microsatellite loci (Van der Strate et al. 2000) to explore fine-scale patch structure and dispersal in C. membranacea. The aims of the present study were to: (i) determine the relative contributions of haploid and diploid individuals including their respective genetic diversities; (ii) assess the contribution of clonal reproduction; (iii) determine the approximate size of genetic individuals within mats; and (iv) estimate small-scale dispersal processes in relation to population differentiation. Materials and methods Study area and sampling design In January 1998, 580 samples of Cladophoropsis membranacea were collected from three different locations on Tenerife and Gran Canaria (Fig. 2). A nested hierarchical sampling design was used in order to assess the spatial scale of differentiation. Cushions were mapped within each 1-m2 quadrat. From each quadrat, 20 samples were taken at random (20 × 4 × 6 = 480 samples). In order to estimate the size of a genetic individual in relation to cushion size, an additional 100 samples (5–18 samples per cushion) were collected at ≈ 1-cm intervals from a range of cushion sizes (≈ 4 – 50 cm). In order to minimize the chance of inadvertently sampling more than one genetic individual from a single cushion, one sample consisted of ≈ 20 filaments plucked from an area of < 0.5 cm2. Filaments were rinsed, blotted dry and placed directly in silica gel for later DNA extraction. DNA extraction DNA was isolated according to the cethyltrimethylammonium bromide (CTAB) protocol of De Jong et al. (1998). Silicadried, algal material (0.02 g) was incubated at 60 °C for 30 min in 500 µL of preheated extraction buffer [2% CTAB (w/v), 1.4 m NaCl, 20 mm ethylenediaminetetraacetic acid, 100 mm Tris–HCl pH 8.0, and 0.2% β-mercaptoethanol (v/v)] followed by a 15-min, slow rotation at room temperature. The crude extract was centrifuged at 2000 g for 15 min and the supernatant was decanted to a fresh tube. The remainder of the extraction followed standard procedures involving two extractions with an equal volume of chloroform– isoamylalcohol (24 : 1, v/v). This was followed by DNA precipitation using two-thirds volume of cold isopropanol (4 °C, 1 h), centrifugation (4 °C, 15 min, 10 000 g), and washing of the pellet with 80% ethanol. The DNA was dissolved in 100 µL of 0.1× TE (10 mm Tris/HCl and 1 mm EDTA pH8). Further purification steps were not required. The typical yield was ≈ 1 µg. Microsatellite amplification and locus visualization We have recently developed microsatellite loci for C. membranacea (Van der Strate et al. 2000). The eight loci Fig. 2 Six study sites, and as an example, the hierarchical sampling design for the location Tenerife south for Cladophoropsis membranacea. © 2002 Blackwell Science Ltd, Molecular Ecology, 11, 329–345 MEC_1448.fm Page 332 Wednesday, February 20, 2002 9:07 AM 332 H . J . V A N D E R S T R A T E E T A L . used in this study are summarized in Table 1. This study represents the first application of these loci. Loci were amplified individually using the polymerase chain reaction (PCR). Each 10-µL reaction contained the following: 2 µL template DNA (≈ 10 ng/µL), 1 µL each of unlabelled, microsatellite primer (5 µm), 1 µL 10 d× NTP mix (2 mm of dATP, dGTP, dTTP and 0.2 mm dCTP; Pharmacia Biotech), 1 µL 10× Taq polymerase buffer (Pharmacia Biotech), 0.08 µL Taq polymerase (5 units/µL, Pharmacia Biotech), 1 µL bovine serum albumin (0.1% w/v) and 0.14 µCi [α32P]dCTP (3000 Ci/mmol, Amersham) in 3 µL H2O. Amplifications were performed in a PTC-100™ machine (MJ Research, Inc.). The profile consisted of an initial denaturation step of 3 min at 94 °C followed by 30 cycles of: 1 min at 94 °C, 2 min at the optimal annealing temperature (Tm) (Table 1), 1.5 min at 72 °C and 10 min at 72 °C. Each PCR run included a positive (2 ng of the plasmid clone DNA containing the microsatellite) and a negative (no template DNA) control. The PCR products were separated by electrophoresis on 5% denaturing polyacrylamide gels (Biozym, Sequagel XR). Loci were visualized using standard autoradiography (medical X-ray film, Fuji Film) and scored manually against a size standard (sequence ladder of the plasmid vector pBluescript SK+) and the amplified clone from the locus of interest (i.e. positive control above). Identification of haploid and diploid individuals Haploid and diploid individuals of C. membranacea cannot be distinguished morphologically. Individuals were considered diploid if any of the eight loci were heterozygous. However, individuals that are homozygous at all eight loci may, in principle, be haploid or diploid. In order to correct for this potential bias, we calculated the expected number of diploid homozygous individuals for all eight loci at each site. This was done by calculating the expected homozygosity for each locus under Hardy–Weinberg equilibrium using the observed allele frequencies and then taking the product of the individual loci times the number of individuals (N = 80). The expected number of eight-locus homozygotes per site was always smaller or, equal to one, indicating that our eight-locus, homozygote assignment to haploids was not biased. Data analysis Genetic diversity was compared separately in the haploid and diploid phases. Basic diversity measures, tests for Hardy–Weinberg equilibrium and F-statistics (Wright 1965) were calculated in the program package genetix ver. 4.0 (Belkhir et al. 1998) or arlequin version. 1.1 (Schneider et al. 1997). Clonal reproduction must be accounted for in population genetic analyses in order to prevent biases in estimates of FIS, FST and linkage disequilibrium. Duplicate haplotypes/diplotypes were therefore used only once. If this is not done, estimates of FIS can be upwardly or downwardly biased depending on whether an excess of homozygotes or heterozygotes is present. Estimates of linkage disequilibrium will also be affected. Withinpopulation differentiation will tend to be downwardly biased, whereas between-population differentiation will tend to be overestimated. Significance testing was carried out using permutation (1000 permutations) followed by sequential Bonferroni correction (Rice 1988). The frequency of expected null alleles was calculated using the method of Brookfield (1996). Clonal diversity (Pd) for each phase was calculated as the proportion of distinguishable haplotypes or diplotypes divided by the total number of samples for the specific phase at the spatial scale of interest (Ellstrand & Roose 1987). A value of 1 indicates that each individual has a unique haplo- or diplotype and therefore, the area has maximal clonal diversity. A value approaching 0 indicates that all individuals have the same haplotype or diplotype (i.e. are monoclonal). Reliable detection of clonality is dependent upon the resolving power of the loci. If a multilocus haplotype or diplotype has many, relatively low-frequency alleles at several loci, the likelihood that it occurs more than once by chance is extremely low. In contrast, if a multilocus haplotype or diplotype is composed of only a few, high-frequency alleles at several loci, the likelihood of multiple occurrences by chance alone may be fairly high. Since we were specifically interested in assessing the clonal contribution to population structure and dispersal, we assessed the resolving power of our eight loci in three ways. The number of unique diplotypes Nd possible is: Nd = Terminology related to haploid and diploid individuals For clarity, we use the term haplotype to refer to the multilocus genotypes of haploid individuals (i.e. free-living gametophytes); and the term diplotype to refer to the multilocus genotypes of diploid individuals (i.e. free-living sporophytes). The term clone is used to refer to identical haplotypes or identical diplotypes that are the result of asexual reproduction of the respective phases. L ∏ [a ( a + 1)] /2 i =1 where L is the number of loci (eight in this study), and ai is the number of alleles at locus i. For haplotypes there is only one allele possible per locus, which means that the number of unique haplotypes Nh present in a given area is the product of all of the possible alleles at the eight different loci. For each eight-locus diplotype (Pdip) the expected probability is: © 2002 Blackwell Science Ltd, Molecular Ecology, 11, 329 – 345 MEC_1448.fm Page 333 Wednesday, February 20, 2002 9:07 AM P O P U L A T I O N S T R U C T U R E O F C L A D O P H O R O P S I S M E M B R A N A C E A 333 Pdip = (Π pi)2h where pi is the frequency in the population of each allele (two per locus) represented in the diplotype and h is the number of loci that are heterozygous (Parks & Werth 1993). For the expected probability of each eight-locus haplotype (Phap) h is set at zero. The above equation also describes the likelihood of occurrence of a given haplotype or diplotype at a given location. If identical haplotypes or diplotypes had P values of < 0.05 and were found in close proximity (e.g. within or between quadrats), they were considered clones. Finally, the likelihood of encountering the same haplotype or diplotype at least twice (Pse) in a more distantly spaced sample was calculated according to: Pse = 1 – (1 – Phap)H, or Pse = 1 – (1 – Pdip)D where H and D are the number of distinct haplotypes and diplotypes identified (Parks & Werth 1993). Linkage disequilibrium was tested for haploid and diploid phases separately. This was done across all 28 [i.e. L(L – 1)/2] possible pairings of loci across all populations and per population (i.e. site) using genepop version. 3.2d (Raymond & Rousset 1995). Linkage disequlibrium was further analysed using the D-statistics of Black & Krafsur (1985) as implemented in genetix version. 4.0 (Belkhir et al. 1998). Significance testing was done using permutation followed by sequential Bonferroni correction (Rice 1988). In order to avoid linkage due to the clonal contribution, duplicate haplotypes and diplotypes were removed prior to analysis. Spatial-autocorrelation was used to estimate clonal dispersal and patch structure from mapped quadrats. Spatial auto-correlation analysis was performed using Moran’s I coefficient in autocorrg version. 2.0 (Hardy & Vekemans 1999). Significance testing per distance class was done using permutation. In order to increase statistical power per class, alternative distance classes were tried, as was combining the four quadrats within a site (including necessary distance corrections). Due to the paucity of diploid individuals, spatial autocorrelation analyses were performed on haploid individuals only. The analysis was first run on the full data set including all duplicated haplotypes and then with the duplicates removed. Population differentiation was investigated at spatial scales of 1, 5 and 20 m and at 5 km (between sites) using a two-level and three-level amova (Excoffier et al. 1992) as implemented the program package arlequin version. 1.1 (Schnieder et al. 1997). Due to the low number of diploids this was done for haploids only. For the two-level amova differentiation was estimated with FST (Weir & Cockerham 1984) and for the three-level analysis FCT and FSC (amova analogues). Duplicate haplotypes/diplotypes were used only once to avoid overestimation of FST. Results Eight microsatellite loci provided a total of 65 alleles (N = 478) (Table 1) of which 35 had a frequency ≥ 0.05 (Fig. 3). Six of the eight loci were moderately to highly polymorphic with expected heterozygosities ranging from 0.59 to 0.89. Consistency of the eight loci and their relative contribution in subsequent calculations was evaluated by computing the jack-knifed mean and standard deviation of FST over all 478 samples (Table 2). Six of the eight loci were found to behave similarly. Loci Cmb5 and Cmb6 were nearly monomorphic and thus contributed little information. In order to assess whether the sampling intensity was sufficient to capture the allelic diversity present, we plotted individuals sampled against the mean number of alleles/ locus (Fig. 4). Even with 20 samples, the major diversity was recovered. Null alleles are a commonly reported problem with microsatellite loci (Hare et al. 1996). This can be the result of Table 1 Microsatellite loci for Cladophoropsis membranacea and their properties based on a sample of N = 478 individuals Locus Repeat Tm (°C) Size range (bp) No. of alleles HE Cmb 1 Cmb 2 Cmb 3 Cmb 4 Cmb 5 Cmb 6 Cmb 7 Cmb 8 Total (GT)6GC(GT)11 (GT)7 GCGGCTACT(GT)18 (GT)12 N26*(GT)14 (GT)4AT (GT)15 (GT)13 (GT)13 (GT)13 (GT)19 60 60 60 60 60 60 55 60 126–136, clone 130 168–186, clone 172 171–185, clone 175 118–136, clone 126 208–212, clone 208 116–120, clone 116 202–228, clone 202 135–161, clone 139 6 10 7 8 3 3 14 14 65 0.70 0.79 0.65 0.59 0.12 0.14 0.83 0.89 0.59 Tm is optimal annealing temperature and HE is unbiased average expected heterozygosity (Nei 1978). See van der Strate et al. (2000) for details. * = AT(CA) (TA) (TG) T(CA) T(AC) . N 26 2 2 3 2 2 © 2002 Blackwell Science Ltd, Molecular Ecology, 11, 329–345 MEC_1448.fm Page 334 Wednesday, February 20, 2002 9:07 AM 334 H . J . V A N D E R S T R A T E E T A L . 0.35 allele frequency 0.4 Locus Cmb 1 Locus Cmb 2 0.30 0.25 0.3 0.20 0.2 Fig. 3 Global allele frequencies for eight microsatellite loci in Cladophoropsis membranacea. Haploid thalli (black, N = 401); diploid thalli (grey, N = 77). Note that y-axes are not the same. 0.15 0.10 0.1 0.05 0.0 0.00 126 128 130 132 136 Locus Cmb 3 0.5 allele frequency 134 168 170 172 174 176 178 0.6 184 186 Locus Cmb 4 0.4 0.3 0.3 0.2 0.2 0.1 0.0 0.0 171 173 175 177 179 181 183 185 118 120 122 124 126 128 130 132 134 136 1.0 1.0 Locus Cmb 6 Locus Cmb 5 allele frequency 182 0.5 0.4 0.1 0.5 0.5 0.0 0.0 208 210 116 212 118 120 0.25 0.30 Locus Cmb 8 Locus Cmb 7 0.25 allele frequency 180 0.20 0.20 0.15 0.15 0.10 0.10 0.05 0.05 0.00 0.00 202 204 206 208 210 212 214 216 218 220 222 224 226 228 135 137 139 141 143 145 147 149 151 153 155 157 159 161 allele size (bp) allele size (bp) Table 2 Consistency of microsatellite loci in Cladophoropsis membranacea. Jack-knifed mean FST values for all haploid samples (without duplicates) over the six sites Mean FST SD FST Cmb 1 Cmb 2 Cmb 3 Cmb 4 Cmb 5 Cmb 6 Cmb 7 Cmb 8 All loci 0.183 0.069 > 0* 0.210 0.079 > 0* 0.279 0.087 > 0** 0.215 0.071 > 0* 0.009 0.021 =0 0.375 0.197 =0 0.166 0.062 > 0* 0.244 0.047 > 0** 0.205 0.015 > 0*** SD, standard deviations. *P < 0.05; **P < 0.01; ***P < 0.001. mutations in flanking sequences that result in failed amplification of one or both alleles. Because we were dependent on molecular identification of haploids vs. diploids, it was critical to assess whether or not nulls could be a significant problem. In our study, all eight loci amplified without difficulty and amplification failure rates were < 0.006. We tested further for null alleles in two ways; first, a set of homozygous individuals was reamplified for all of the © 2002 Blackwell Science Ltd, Molecular Ecology, 11, 329 – 345 MEC_1448.fm Page 335 Wednesday, February 20, 2002 9:07 AM Mean number of alleles/locus P O P U L A T I O N S T R U C T U R E O F C L A D O P H O R O P S I S M E M B R A N A C E A 335 6 5 4 3 Playa del Hombre Penascos Palm-Mar Las Galletas La Barranquera Punta del Hidalgo all 2 1 0 0 10 20 30 40 50 60 70 80 Number of individuals Fig. 4 Relationship between sampling effort and mean number of alleles per locus for the six sites, plotted separately. different loci under relaxed annealing temperatures. No additional alleles were amplified. Second, we calculated the expected frequency of null alleles for diploid individuals according to equation (4) of Brookfield (1996) (Table 3). These values were all less than one. Although neither of these tests is foolproof, we could find no evidence that homozygous individuals were the result of null alleles. The number of alleles per locus ranged from 3 to 14 with an overall mean of 7.6 alleles per locus for the haploid individuals and 6.8 alleles per locus in the diploid individuals (Table 3). This difference is not significant (two-sample t-test). Likewise, allele frequencies between haploids and diploids were not significantly different within sites (exact test for population differentiation). There were no haploid/diploid- specific alleles detected that might be suggestive of different gene pools. Diploid populations were not in Hardy–Weinberg equilibrium as assessed by significantly positive FIS values (Table 3) at five of the six sites (diplotypes used once; duplicates removed). Although diploid sample sizes were small in most cases, those at Las Galletas (N = 16) and La Barranquera (N = 25) still maintained high values of heterozygote deficiency across loci. Thirteen out of 28 pairwise comparisons among the eight loci revealed significant linkage disequilibrium (LD) (Table 4). Further testing revealed that LD in the haploid phase was due to drift (DIS < DST and D’IS < D’ST) and not systematic selection (notation of Black & Krafsur 1985). LD was found at all sites in the haploid phase and at La Barranquera in the diploid phase (Table 4). The apparent absence of LD at the other sites probably reflects insufficient sample sizes. Haploids, diploids and clones Among the 478 samples taken, 401 were found to be haploid and 77 diploid (Table 3). The chance that plants assigned as haploids might actually be fully homozygous diploids was extremely low (Table 3). Therefore we are confident that the number of haploids observed is a good estimate of the true condition, in which haploid plants greatly outnumbered diploid plants at all six sites. At Peñascos this was nearly 10 : 1 whereas at La Barranquera it was 2 : 1. Even when identical haplotypes and diplotypes were subsequently Table 3 Comparison of the clonal diversity (Pd), per cent polymorphic loci (P; 99% criterion), mean number of alleles per locus (NA) and genetic diversity (HE, expected heterozygosity) between haploid (1n) and diploid (2n) thalli of Cladophoropsis membranacea at six sites Location Site Gran Canaria Playa del Hombre Peñascos Tenerife south Palm-Mar Las Galletas Tenerife north La Barranquera Punta del Hidalgo Overall Life history phase No. of indiv. Diploid homoE n 2n n 2n n 2n n 2n n 2n n 2n n 2n 71 9 76 4 70 10 62 16 55 25 67 13 401 77 0.03 1.18 0.92 0.82 0.18 0.32 No. of indiv. minus clonality Pd P(%) NA HE 40 9 37 4 41 10 25 16 41 24 42 13 219 76 0.56 1 0.49 1 0.59 1 0.40 1 0.75 0.96 0.63 1 0.55 0.98 100 100 100 75 87.5 75 75 87.5 100 87.5 100 87.5 100 100 5.6 3.9 5.4 2.9 4.0 2.8 3.3 3.1 3.6 3.9 4.3 3.8 7.6 6.8 0.64 0.56 0.51 0.49 0.46 0.38 0.42 0.38 0.50 0.48 0.49 0.44 0.62 0.59 HO NullsE FIS 0.31 <1 0.53 <1 0.25 <1 0.36*** 0.21 <1 0.44*** 0.26 1 0.45*** 0.23 <1 0.49*** 0.26 <7 0.47*** – 0.10 The number of expected diploid homozygotes (HomoE) per site is 1.2 (see Materials and methods section). Observed heterozygosity (HO), NullsE (Brookfield 1996) and the inbreeding coefficient (FIS) are calculated for diploids. ***P < 0.001. © 2002 Blackwell Science Ltd, Molecular Ecology, 11, 329–345 MEC_1448.fm Page 336 Wednesday, February 20, 2002 9:07 AM 336 H . J . V A N D E R S T R A T E E T A L . Table 4 Results of Fisher’s exact test for linkage disequilibrium as implemented in genepop version 3.2 (Raymond & Rousset 1995) Pairwise comparison of loci Locus Cmb 1 Cmb 1 Cmb 2 Cmb 3 Cmb 4 Cmb 5 Cmb 6 Cmb 7 Cmb 8 — *** — — — — — Linkage disequilibrium per site Cmb 2 Cmb 3 Cmb 4 Cmb 5 Cmb 6 Cmb7 Cmb 8 Site Haploids Diploids *** *** *** *** *** — — — — — — *** — — — *** *** — *** — *** *** *** *** — — — — Playa del Hombre Peñascos Palm-Mar Las Galletas La Barranquera Punta del Hidalgo 12/28 (40) 11/28 (37) 1/21 (41) 5/15 (25) 5/28 (41) 2/28 (42) 0/28 (9) 0/6 (4) 0/15 (10) 0/21 (16) 4/21 (24) 0/21 (13) — — — — — — — — — — — — — — — — — — — — — Pairwise comparison of loci (Cmb 1 to Cmb 8) across all the six sites for Cladophoropsis membranacea. Haploids (upper right) and diploids (lower left) were treated separately. Duplicated clones were removed. Right: number of pairwise comparisons across loci showing linkage disequlibrium per site. Calculations for diploids are questionable due to small sample sizes at most sites. Duplicate clones were removed. Sample sizes in parentheses ***P < 0.001 after Bonferroni correction. removed, the ratio still ranged from 4 : 1 to 2 : 1 in favour of haploids. Within-site clonal diversity varied between 25 and 60% for haploids. Cladophoropsis membranacea can reproduce either the diploid or haploid phases through asexual production of spores. This contributes yet another element to the population structure, which had to be identified. Using the observed allele frequencies for each locus, the possible number of unique eight-locus haplotypes (Nh) was 3.3 × 106 and the number of possible unique diplotypes (Nd) was 1.79 × 1010. We identified 219 unique haplotypes and 76 unique diplotypes. An additional 65 haplotypes and only one diplotype (La Barranquera) occurred two or more times. These were considered clones (or duplicates). Clonal diversity (Pd) was high, ranging from 0.40 to 0.75 (x̄ = 0.55) for the haploid phase and from 0.96 to 1.0 (x̄ = 0.99) for the diploid phase over the six sites. The haploid phase contained a significantly higher number of clones per site then the diploid phase (P = 0.0003, t-test). As illustrated in Table 5, between nine and 15 clonal haplotype types were detected per site and most were unique for a given site. Although the calculated values of Nh and Nd were large, the presence of a few alleles in high frequencies at each locus might significantly reduce these numbers and lead to the occurrence of identical multilocus haplotypes/ diplotypes by chance alone. In order to assess this factor we calculated the probabilities of occurrence Pgen and Pdip for all haplotypes and diplotypes that were found more than once (Table 5). In 100% of the cases the probabilities were < 0.05 and in > 80% of the cases they were < 0.001. This meant that the likelihood of any eight-locus haplotype or diplotype occurring by chance was extremely low. Thus we attributed identical eight-locus, microsatellite haplotypes or diplotypes to asexual reproduction, especially if the individuals were in close proximity. However, some identical haplotypes were found at scales of 5 – 26 m, as illustrated in Fig. 5. These individuals may or may not be dispersed clones based on probabilities of second encounter (Pse). Although this calculation is somewhat circular (because higher haplotype frequencies will increase the chance of encounter), it does provide some indication of where dispersal boundaries might be expected, especially when used in conjunction with spatial auto-correlation and spatial-hierarchical analyses of population differentiation. As shown in Table 5, more than half of the Pse values are much larger than 0.05 and most of these occurred at distances of > 5 m. At Playa del Hombre and Peñascos, for example, only two identical haplotypes (Fig. 5, dark blue and light blue cushions) were found between quadrats (> 5 m) and in three cases at distances > 20 m (Fig. 5 blue, red and purple cushions). Over the entire study, identical haplotypes were found at distances > 5 km (between sites) in only seven cases. Mats and individuals Individual thalli of C. membranacea coalesce with one another to form small cushions or more extensive mats. In order to investigate the clonal diversity of a mat, we sampled several cushions of different sizes as exemplified in Fig. 6. Eight-locus haplotypes showed that cushions of ≈ 1– 5 cm in diameter were typically one genetic individual (N = 3 cushions, 15 samples). Cushions 7 –10 cm in diameter contained two haplotypes (N = 2 cushions, 10 samples). In mats (> 50 cm), up to six haplotypes and eight genotypes were detected (N = 3 mats, 54 samples). Mats thus represent a mixture of different genetic individuals and are not single, fast-growing clones. © 2002 Blackwell Science Ltd, Molecular Ecology, 11, 329 – 345 MEC_1448.fm Page 337 Wednesday, February 20, 2002 9:07 AM P O P U L A T I O N S T R U C T U R E O F C L A D O P H O R O P S I S M E M B R A N A C E A 337 Table 5 Clones in Cladophoropsis membranacea Haplotype Frequency Phap Table 5 Continued Pse Gran Canaria Playa del Hombre 1 13 2 4 3 4 4 4 5 3 6 2 7 2 8 2 9 2 10 2 11 2 12 2 13 2 14 1 15 1 0.0003 0.0005 7.6E-05 0.0003 1.0E-05 5.1E-05 4.4E-05 4.6E-05 0.0001 2.0E-08 2.8- 05 9.1E-07 0.0001 0.0003 0.0009 0.0133 0.0216 0.0031 0.0109 0.0004 0.0020 0.0017 0.0018 0.0046 8.1E-07 0.0011 3.6E-05 0.0054 0.0115 0.0349 Peñascos 1 2 10 14 15 16 17 18 19 20 0.0147 0.0250 4.2E-07 0.0029 0.0125 0.0078 8.4E-05 0.0046 0.0033 1.6E-06 0.4225 0.6087 1.5E-05 0.1003 0.3726 0.2522 0.0031 0.1569 0.1140 5.8E-05 17 8 2 2 6 4 3 3 2 2 Tenerife south Palm-Mar 21 22 23 24 25 26 27 28 29 30 31 32 33 10 5 4 4 4 3 2 2 2 2 2 1 1 0.0207 0.0055 0.0097 0.0103 0.0087 0.0031 0.0098 0.0058 0.0003 2.5E-07 0.0017 0.0010 0.0015 0.5763 0.2009 0.3294 0.3450 0.3018 0.1179 0.3327 0.2123 0.0138 1.0E-05 0.0666 0.0385 0.0609 Las Galletas 32 33 34 35 36 37 38 39 40 41 42 5 4 10 10 4 3 3 3 2 2 2 0.0030 0.0151 0.0302 0.0013 0.0181 0.0085 0.0002 0.0038 0.0004 0.0027 0.0151 0.0729 0.3167 0.5357 0.0315 0.3671 0.1928 0.0053 0.0904 0.0106 0.0658 0.3166 © 2002 Blackwell Science Ltd, Molecular Ecology, 11, 329–345 Haplotype Frequency Phap Pse Tenerife north La Barranquera 43 44 45 46 47 48 49 50 51 D 4 3 3 3 2 2 2 2 2 2 0.0034 0.0004 0.0002 0.0011 0.0051 0.0059 0.0102 6.4E-05 0.0008 1.4E-05 0.1298 0.0182 0.0073 0.0441 0.1885 0.2163 0.3421 0.0026 0.0327 0.0003 Punta del Hidalgo 52 53 54 55 56 57 58 59 60 61 62 63 64 65 5 4 3 3 3 3 3 3 2 2 2 2 2 2 0.0150 0.0115 0.0099 0.0081 0.0129 0.0007 7.7E-06 0.0002 0.0001 7.8E-05 0.0002 0.0029 0.0008 0.0062 0.4704 0.3844 0.3417 0.2891 0.4198 0.0292 0.0003 0.0097 0.0043 0.0032 0.0073 0.1161 0.0334 0.2294 Sixty-five distinct multilocus haplotypes that occurred more then once and their estimated probability of encounter (Phap) and reencounter (Pse). Haplotypes in bold were found between the sites. The only diplotype (D) that occurred more then once was found at La Barranquera. Dispersal At each site individuals were mapped within quadrats from which a spatial autocorrelation analysis was performed (Fig. 7). Individuals in closer proximity to one another, i.e. in smaller distance classes, were expected to share a higher correlation of alleles. In the first analysis, all haplotypes were included. A comparison of all sampled haplotypes (Fig. 7, solid lines) reveals a significant correlation at up to 80 cm at four of the six sites. The intercept of the x-axis is taken as the approximate radius of the patch size of dispersal. At Playa del Hombre, for example, this suggests clonal dispersal of ≈ 1.2 m. When duplicate clones were removed so that each haplotype was counted only once in the analysis (Fig. 7, dotted lines), there was no correlation. This suggests that dispersal has two components: the initial random recruitment at the site followed by asexual amplification of the resident thalli to ‘fill-in’ the space. Fig. 5 Mapped quadrats of Cladophoropsis membranacea cushions at Playa del Hombre (top) and Peñascos (bottom). Uncoloured and numbered cushions contain unique eight-locus haplotypes or diplotypes. Within Playa del Hombre or within Peñascos, cushions with the same colour contain identical eight-locus haplotypes. MEC_1448.fm Page 338 Wednesday, February 20, 2002 9:07 AM 338 H . J . V A N D E R S T R A T E E T A L . © 2002 Blackwell Science Ltd, Molecular Ecology, 11, 329 – 345 MEC_1448.fm Page 339 Wednesday, February 20, 2002 9:07 AM P O P U L A T I O N S T R U C T U R E O F C L A D O P H O R O P S I S M E M B R A N A C E A 339 Table 6 Overview of diploid individuals of Cladophoropsis membranacea assignable to parents present within the same quadrat Parents assignable Fig. 6 Relationships between thallus size and individuality in Cladophoropsis membranacea. (A) A 50-cm long, continuous mat was sampled at the points shown. (B) Schematic representation of the mat in (A) and of three other cushions each sampled five times. Colours correspond to haplotypes in haploid plants (d) and diplotypes in diploid plants (j). Where diploid plants were identified, we examined whether or not they could be assigned to nearby haploid parents from the same quadrat (1 m2). About 50% could be assigned to one or both parents (Table 6). Population differentiation At each site we tested for population differentiation at three scales; 1, 5 and 20 m. With the exception of La Barranquera, there was no significant population differentiation detected at these scales (Table 7). Using a two level amova we also tested for differences between sites. In all three cases, significant FST values were found at 6 –10 km. Approximately 90% of the variance was accounted for within sites and only about 10% between sites. Discussion Haploid and diploid plants were found at all sites but haploid plants were always dominant and the two phases were not in Hardy–Weinberg equilibrium as shown by heterozygote deficiencies and significant linkage disequilibrium. © 2002 Blackwell Science Ltd, Molecular Ecology, 11, 329–345 Site No.of diploids both one none Playa del Hombre Peñascos Palm-Mar Las Galletas La Barranquera Punta del Hidalgo 9 4 10 16 24 13 3 0 0 1 1 1 1 2 6 8 11 4 5 2 4 7 12 8 Total 76 6 32 38 The chance for inbreeding is probably high in Cladophoropsis membranacea. This is because dispersal distances for gametes/ spores are short (≈ 1 m), the local dominance of a few clones would reduce the effective population sizes considerably (Table 3) and because the haploid phase is the gametophyte. Playa del Hombre (Fig. 5) typifies such a setting in which 71 of 80 individuals were haploid. Of these, 31 haplotypes occurred just once, 15 occurred more than once and one haplotype occurred 13 times. If there are no barriers to selfing, the opportunities for outcrossing would be further reduced as suggested by parental assignment of diploids in Table 6. While inbreeding is most likely, heterozygote deficiencies can also be the result of a Wahlund effect, null alleles or sampling artefacts. A Wahlund effect is unlikely given the small spatial scale of the study and the lack of population differentiation at scales < 5 km. Null alleles are unlikely based on tests presented in the Results section. Small diploid sample sizes might have led to spurious results in cases where N was very small, but results from La Barranquera (N = 24) suggest that heterozygote deficiencies are real. Linkage disequilibrium was attributed to genetic drift. However, the nature of small-scale population dynamics in C. membranacea may be promoting the disequilibrium via small effective population sizes, i.e. founder events, few diploids and low clonal diversity of the haploids and nonrandom mating. Populations may also be in a permanent state of nonequilibrium. Since drift is expected to be stronger in small populations, we looked for correlations between linkage disequilibrium and clonal diversity, i.e. stronger disequilibrium expected at those sites having the lowest clonal diversity (Tables 3 and 4). No correlations were found. The only other report of linkage disequilibrium in seaweeds is in Gelidium arbuscula (Sosa et al. 1998). There it was attributed to significant differences in allele frequencies found between sporophytes and gametophytes combined with dominant asexual reproduction. The high genetic diversity found in both phases of C. membranacea and the lack of differences in allele frequencies indicates that the two MEC_1448.fm Page 340 Wednesday, February 20, 2002 9:07 AM 340 H . J . V A N D E R S T R A T E E T A L . 0.5 0.6 * Playa del Hombre * 0.4 Penascos 0.4 Moran’s I Moran’s I 0.3 * * 0.2 0.1 * 0.2 * 0.0 0.0 –0.2 –0.1 –0.2 –0.4 0 20 40 60 80 100 120 140 0 20 Central radius of distance class (in cm) 60 80 100 120 140 0.3 0.4 * La Barranquera 0.3 * * * 0.1 * 0.2 Moran’s I * 0.2 Moran’s I 40 Central radius of distance class (in cm) Punta del Hidalgo ** 0.1 * 0.0 0.0 –0.1 –0.1 * –0.2 –0.2 0 20 40 60 80 100 120 0 140 20 40 60 80 100 120 140 Central radius of distance class (in cm) Central radius of distance class (in cm) 0.4 0.5 Palm-Mar * 0.2 Las Galletas 0.4 Moran’s I Moran’s I 0.3 0.0 –0.2 0.2 0.1 0.0 –0.1 –0.4 –0.2 –0.6 –0.3 0 20 40 60 80 100 120 140 Central radius of distance class (in cm) 0 20 40 60 80 100 120 140 Central radius of distance class (in cm) Fig. 7 Spatial auto-correlation plots for all haploid thalli of Cladophoropsis membranacea at each site. Solid lines (all samples); dotted lines (duplicate clones removed); * significant spatial auto-correlation at P < 0.05 for specified distance class. phases are sufficiently refreshed by sexual reproduction to prevent loss of one or both stages. An interesting and, as yet unresolved, question is whether C. membranacea is actually a perennial alga that dies back each year but regenerates from microscopic, over-wintering thalli. In that case, the balance of diploids and haploids may depend more on chance events of initial recruitment and subsequent density-dependent factors. Future studies will test for temporal stability or lack thereof. Dominance of the haploid phase Only a few studies have investigated the proportions of isomorphic haploid and diploid plants under field conditions. As shown in Fig. 6, cushions and mats are composed of multiple haploid, diploid, or clonal individuals with haploids dominating. Studies in two rhodophytic seaweeds from the Canary Islands, Gelidium canariensis (Sosa & Garcia-Reina 1993) and in Gelidium arbuscula (Sosa & Garcia-Reina 1992) showed a permanent dominance of the diploid phase over a 2-year period in both species and significant differences in allele frequencies between the two phases in some populations of G. arbuscula (Sosa et al. 1998). Equal distributions of haploids and diploids have also been reported in Gracilaria gracilis (Engel et al. 1999) and in Gracilaria verrucosa (now: gracilis) (Destombe et al. 1989). In both species an excess of haploids was observed only transiently over a 1-month period. All of these species, however, are relatively long-lived plants that persist for several years. They also © 2002 Blackwell Science Ltd, Molecular Ecology, 11, 329 – 345 MEC_1448.fm Page 341 Wednesday, February 20, 2002 9:07 AM P O P U L A T I O N S T R U C T U R E O F C L A D O P H O R O P S I S M E M B R A N A C E A 341 Table 7 Hierarchical amova analysis of spatial scales of differentiation in Cladophoropsis membranacea Source of variation Scale d.f. Variance components Per cent variation Fixation indices (FCT, FSC, FST) P value between plots within a site between quadrats within a plot within quadrats 20 m 4.5–5 m 1 m2 1 2 41 0.05335 –0.06774 2.56379 2.09 –2.66 100.56 0.02093 –0.02714 –0.00564 0.33920 0.84066 0.67644 Peñascos between plots within a site between quadrats within a plot within quadrats 16 m 4–6 m 1 m2 1 2 42 –0.06018 0.06098 1.83996 –3.27 3.31 99.96 –0.03269 0.03208 0.00044 0.66471 0.10948 0.26686 PdH and Peñ between sites within sites 6.8 km 26–29.5 m 1 89 0.17541 2.19363 7.40 92.60 between plots within a site between quadrats within a plot within quadrats 20 m 2.5–5 m 1 m2 1 2 45 0.21418 –0.00033 1.89437 10.16 –0.02 89.86 0.10159 –0.00017 0.10144* 0.33724 0.41349 0.01271 Punta del Hidalgo between plots within a site between quadrats within a plot within quadrats 21 m 2.6–4 m 1 m2 1 2 46 –0.04415 0.07245 1.91459 –2.27 3.73 98.54 –0.02272 0.03646 0.01457 1.00000 0.07527 0.11926 LB and PH between sites within sites 10 km 27.5–27.6 m 1 94 0.37990 1.97417 16.14 83.86 between plots within a site between quadrats within a plot within quadrats 22 m 4.5–6 m 1 m2 1 2 49 0.00612 –0.00889 1.83131 0.33 –0.49 100.15 0.00335 –0.00488 –0.00151 0.33333 0.52297 0.48778 Las Galletas between plots within a site between quadrats within a plot within quadrats 21 m 6.4–7 m 1 m2 1 2 41 –0.01060 –0.00742 1.61212 –0.66 –0.47 101.13 –0.00665 –0.00462 –0.01130 0.30401 0.45748 0.65200 PM and LG between sites within sites 8.1 km 32.5–34.4 m 1 93 0.29093 1.72775 14.41 85.59 Site Gran Canaria Playa del Hombre Tenerife North La Barranquera Tenerife South Palm-Mar 0.07404*** 0.16138*** 0.14412*** 0.00000 0.00000 0.00000 Only haploid thalli were used and duplicate haplotypes were counted only once. Small negative values can occur by chance because individuals being drawn at random from one group/subgroup have a higher probability of being identical to an individual from another group/subgroup of origin (Excoffier et al. 1992). *P < 0.05; ***P < 0.001 after Bonferroni correction. possess an additional life history stage involving a diploid carposporophyte stage, which mitotically amplifies the diploid stage in a manner analogous to the haploid stage in C. membranacea. The finding that haploid thalli of C. membranacea accounted for 84% of the samples and outnumbered diploid thalli by at least 2 : 1 (and sometimes as much as 10 : 1) was not expected at the outset of the study. Although plant biomass waxes and wanes throughout the year, the balance between life history stages had been expected to be relatively even. At least three explanations may account for why this was not so. First, differences in habitat requirement between gametophytes and sporophytes might result in a biased sampling. This is known to be important for heteromorphic seaweed species such as the rhodophyte Asparagopsis/Falkenbergia where gametophytes are subtidal and the sporophytes © 2002 Blackwell Science Ltd, Molecular Ecology, 11, 329–345 intertidal. In C. membranacea, however, plants do not occur in the subtidal or in the very high intertidal zones. This leaves only the possibility of nonapparent microhabitat heterogeneity within the relatively narrow zone in which it occurs. In Enteromorpha, an alga with a similar isomorphic life history and habitat, Joint et al. (2000) performed laboratory experiments in which they found that diploid spores preferentially settled on bacterial films. This type of phase-specific resource partitioning may play a substantial role in determining which part of the life history can recruit. Unfortunately, it will be very difficult to assess in field populations without prior knowledge of the resources being competed for. Second, seasonality might also provide an explanation for the different proportions of haploid and diploid plants. All sampling was conducted in January and thus represents a single time point. During the summer months, shifts in temperature and general exposure of reefs result in senescence MEC_1448.fm Page 342 Wednesday, February 20, 2002 9:07 AM 342 H . J . V A N D E R S T R A T E E T A L . and die-back of C. membranacea that may lead to its apparent disappearance at some sites. Although reproduction appears to be continuous, the specific type of reproduction (i.e. sexual or asexual) is actually not known. There are no specialized gametangia or sporangia, and biflagellate gametes and quadriflagellate spores can only be distinguished under the microscope. Thus, field identification of reproductive plants is, by itself, insufficient. Repeat sampling of the study sites at other times throughout the year could, in principle, reveal a temporal dominance of diploids, especially if this could be related to nutrient availability. Third, the dominance of haploids might also reflect competitive advantage with or without seasonality. Locally adapted haplotypes that propagate asexually may rapidly minimize the availability of unoccupied space and thus limit or even prevent opportunities for recruitment of new diplotypes via sexual reproduction. This phenomenon has been documented in (semi)aquatic plants (Grace 1993; Neuhaus et al. 1993), and in corals (Hunter 1993). In algae, there is at least some evidence for competitive dominance in Gracilaria verrucosa (Destombe et al. 1993). They compared competitive abilities between isomorphic haploid and diploid thalli and found that haploids grew better than diploids in low-nutrient conditions. They concluded that haploid-competitive advantage would allow them to dominate under a broad range of environmental conditions. Cladophoropsis membranacea may follow a similar pattern in which more stressful conditions in the late summer and autumn favour the haploid phase. Modelling studies (Hughes & Otto 1999) show that asexual reproduction of the haploid phase is low cost to the plant and may even provide a selective advantage to the persistence of the species. For example, advantageous alleles would be exposed to direct selection in haploids while any deleterious alleles carried during the diploid phase could be rapidly purged during the haploid phase. Even a small amount of sexual reproduction is sufficient to maintain genetic diversity, therefore making the numerical dominance of haploid plants at any given time unimportant. Initial dominance Spatial auto-correlation analysis showed that haploid and diploid individuals (i.e. duplicate haplotypes or diplotypes removed) were randomly distributed. This implies that the initial recruitment at a site is simply dependent on the mix of gametes and spores in the propagule pool. An initial skew one way or the other would simply change the rate at which a mature patch would come to be dominated by haploids or diploids. Since clonal reproduction of the haploids accounted for between 50 and 75% of the individuals, density-dependent effects on subsequent recruitment are likely to play a significant role under our competitive superiority hypothesis as long as the local area remains environmentally stable. This would be especially true if microscopic stages of C. membranacea are able to over-winter in the porous substrata. Many algae on (sub)tropical reefs are viewed as ephemeral components of the intertidal turf community and assumed to be annuals. Whether or not the same clonal haplotypes persist year after year, or are replaced by a new set of haplotypes from near by or far away is not known. Perennial microscopic forms and propagule banks have been postulated many times for seaweeds but their actual presence is very difficult to prove (Norton 1992a; Santelices et al. 1995). Such microscopic reserves in the substratum could differentially respond to environmental selection pressures and would go a long way towards testing the fundamental question of population persistence since natural environmental fluctuations in the intertidal are expected to select for more than a few haplotypes/ diplotypes on a long-term basis. Dispersal Short- and long-distance dispersal affect population structure differently. Most studies of direct dispersal of algal gametes and spores, including the present study, have shown that dispersal is limited to a few metres. In Gracilaria verrucosa, the viability of male gametes is restricted to 6 h and dispersal within 2 m (Destombe et al. 1990, 1992). In Gracilaria gracilis 80% of the actual mate pairs were separated by < 1 m (Engel et al. 1999). Nevertheless, 11% of the cystocarps were attributed to foreign males, probably from a population 25 m away. Fingerprinting analyses in the sea palm kelp Postelsia palmaeformis indicated spore dispersal of 1– 5 m (Coyer et al. 1997) and a microsatellite study in the fucoid Ascophyllum nodosum indicated dispersal of 70 cm (Olsen unpublished). Wave-swept environments may actually retard dispersal by maintaining a kind of retention zone in which the local spore/propagule pool is trapped in tidepools and pockets (Coyer et al. 1997; Engel et al. 1999; Wright et al. 2000). An exception to the short-distance generalization is found in the green alga Enteromorpha linza. Innes (1987) was able to track spores for at least 200 m and Zechmann & Mathieson (1985) showed that green algal gametes, spores and zygotes were more often found in surface water samples along the coast of New Hampshire (USA) than were gametes, spores and zygotes from rhodophytic or phaeophytic seaweeds. In C. membranacea, a few identical haplotypes were found at a distance of 20 m and, in seven cases, between sites 5–10 km apart. While the 20-m scale fits with the observations of Zechmann & Mathieson (1985), the larger scale remains difficult to interpret. We know that gene flow occurs at these scales as shown by significant population differentiation (FST 0.07–0.16; P < 0.001) in Table 7. However, it is not possible to distinguish whether our observations represent © 2002 Blackwell Science Ltd, Molecular Ecology, 11, 329 – 345 MEC_1448.fm Page 343 Wednesday, February 20, 2002 9:07 AM P O P U L A T I O N S T R U C T U R E O F C L A D O P H O R O P S I S M E M B R A N A C E A 343 true long-distance dispersal of gametes/spores or a chance occurrence of the same multilocus haplotype. At these distances the role of plant fragments, either rafted or floating probably plays the key role. Although fragments of C. membranacea are unlikely to reattach, spores can be released at any time and floating debris containing C. membranacea is relatively common. Whole-plant dispersal may therefore play a role at intermediate distances, thus augmenting the limits of spore dispersal. It may also account for the relatively weak isolation by distance observed around and between islands (Van der Strate unpublished). Biphasic life histories as an evolutionary stable strategy The persistence of species with free-living haploid and diploid stages has generally been viewed as a transitory, evolutionary state (Maynard Smith 1978; Stebbins & Hill 1980) in the evolution towards diploidy. However, recent theoretical modelling suggests that biphasic life histories represent an evolutionary stable strategy (ESS) (Kondrashov & Crow 1991; Bengtsson 1992; Richerd et al. 1993, 1994; Otto & Marks 1996) and that seaweeds are able to maintain it indefinitely across many lineages (Valero et al. 1992; Klinger 1993; Hughes & Otto 1999). Diploids are thought to have an automatic fitness advantage over haploids because they have two copies of every gene and are better able to survive the effects of deleterious mutations. In contrast, deleterious mutations in haploid individuals will be more rapidly eliminated by selection and advantageous mutations may confer greater local fitness. Species able to switch between these two modes clearly have an advantage. Otto & Marks (1996) were able to show in their modelling simulations that assortative mating, selfing and apomixis acted to maintain genetic associations that favoured the haploid phase; whereas conditions that promoted random mating and outcrossing favoured diploidy. More recently, Hughes & Otto (1999) developed a combined model allowing for life-cycle differences and competition which allowed them to explore the effects of ecological factors on the maintenance of biphasic life histories in organisms with isomorphic haploid and diploid stages. They found that linked reproductive phases had few confounding effects on competition, and if an environment could be exploited more efficiently by haploids and diploids, then these two entities could coexist in an evolutionarily stable strategy. They also explored the conditions that favoured shifts between haploidy and diploidy. Using demographic data from the isomorphic alga Gracilaria (Destombe et al. 1993) they found that competitive abilities of haploids could overcome the advantages of being diploid when niche differentiation and haploid resistance to competition were sufficient to compensate for higher diploid survival and reproduction, but not so great that diploids were lost altogether. To test the Hughes & Otto (1999) model with C. membranacea © 2002 Blackwell Science Ltd, Molecular Ecology, 11, 329–345 would require detailed information about the demography and competitive interactions between the two isomorphic phases which is currently unavailable. Using a combination of indirect genetic data with demographic data from the field it should be possible to test the life-history part of the model. Designing experiments to test competition, however, will probably be limited to laboratory experiments. In conclusion, high-resolution genetic markers have allowed us to explore population structure in a common tropical marine alga characterized by an isomorphic, biphasic life history. The proportions of haploids, diploids and clones suggests dominance of the haploid phase and its probable competitive superiority. Future studies must add a temporal component. The importance of seasonality (or lack thereof ), persistence vs. new recruitment (possibly from propagule banks) and competition between phases needs to be assessed. There is also a critical need for demographic data. With microsatellites it is now possible to follow fertility and distinguish haplotypes and diplotypes in the field. Acknowledgements We thank Ricardo Haroun for arranging and assisting with the field work on Gran Canaria and Tenerife. We also thank Pedro Sosa, Mark Vermeij and Rike Walda for assistance with the fieldwork, and Stella Boele-Bos for assistance with the laboratory analyses. 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