Temporal and spatial variation in the distribution of life history phases of <italic>Chondrus crispus</italic> (Gigartinales, Rhodophyta)<sup>#</sup>
Temporal and spatial variation in the distribution of life history phases of Chondrus crispus (Gigartinales, Rhodophyta)#
ALGAE. 2011. Jun, 26(1): 61-71
Copyright ©2011, The Korean Society of Phycology
This is an Open Access article distributed under the terms of theCreative Commons Attribution Non-Commercial License( permits unrestrictednon-commercial use, distribution, and reproduction in any medium,provided the original work is properly cited.
  • Received : January 10, 2011
  • Accepted : February 19, 2011
  • Published : June 30, 2011
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About the Authors
David J. Garbary
Department of Biology, St. Francis Xavier University, Antigonish, NS B2G 2W5, Canada
Elizabeth Tompkins
Department of Biology, St. Francis Xavier University, Antigonish, NS B2G 2W5, Canada
Katelyn White
Department of Biology, St. Francis Xavier University, Antigonish, NS B2G 2W5, Canada
Peter Corey
Department of Plant and Animal Sciences, Nova Scotia Agricultural College, Truro, NS B0W 2E0, Canada
Jang K. Kim
Department of Plant and Animal Sciences, Nova Scotia Agricultural College, Truro, NS B0W 2E0, Canada

Thirty populations of Chondrus crispus Stackhouse from Nova Scotia were collected during the years 1993 to 2011.Taken from estuaries, wave exposed open coasts, high intertidal rock pools and shallow subtidal habitats, the populations were evaluated for relative abundance of tetrasporophytic and gametophytic life history phases. Over 2,800 thalli were characterized using the resorcinol-acetal test to distinguish the kappa- and lambda-carrageenan containing fronds of gametophytes and tetrasporophytes, respectively. These populations had 77 ± 5% gametophytes (mean ± 95% confidence interval), with most populations having gametophyte : sporophyte ratios ranging from 2 : 1 to 9 : 1. No population had a dominance of tetrasporophytes, although two populations had 1 : 1 ratios. A meta-analysis of our data along with previously published accounts showed no significant changes in gametophyte dominance with respect to hypothesized gradients of wave exposure, salinity, or water depth. Significant changes occurred in ratios at five sites where replicate sampling occurred in different years. We conclude that C. crispus in Maritime Canada has a natural ratio of 3 : 1 or greater in stable conditions, and that lower ratios represent recovery from disturbance in which bare substratum is created that is subsequently colonized by carpospores from remaining gametophytic thalli.
The life history of Chondrus crispus Stackhouse (Irish moss) consists of isomorphic generations in which gametophytic(male and female) and tetrasporophytic thalli produce clonal individuals in which numerous fronds arise from a crustose base (Taylor 1962, Mathieson and Prince 1973, Mathieson and Burns 1975, Sharp 1987, McLachlan et al. 1989, McLachlan 1991). The thalli are perennial and have a wide range of frond sizes and morphologies, with only the few largest fronds on each thallus being reproductive (e.g., Bhattacharya 1985, Bird and McLachlan 1992). Following reproduction, the large fronds are lost from the thallus to be succeeded by other fronds that will replace them, and in turn become reproductive.The species is abundant in eastern Canada where it is economically important based on wild harvests that are collected in both Nova Scotia and Prince Edward Island for extraction of carrageenan (e.g., MacFarlane 1952,McLachlan et al. 1987, McLachlan 1991, Bird and van der Meer 1993). Furthermore, land-based aquaculture of C.crispus has proven successful in the production of food for human consumption (Acadian Seaplants Ltd., www
Like other members of the Gigartinaceae, C. crispus produces different forms of carrageenan in the two life collechistory phases, i.e., primarily kappa-carrageenan in gametophytic thalli and lambda-carrageenan in tetrasporophytic thalli (Chen et al. 1973, McCandless et al. 1973, McCandless 1981, Chopin 1986). Yaphe and Arsenault (1965) initially proposed a colorometric method for distinguishing the 3, 6-anhydrogalactose that characterizes kappa-carrageenan, and this was later modified for general applications by Craigie and Leigh (1978), Dyck et al. (1985) and Garbary and De Wreede (1988). The technique has proven invaluable in many ecological studies of Gigartinaceae where there is an interest in determining the relative abundance of haploid and diploid phases and the causal factors behind apparent differences in their abundance (e.g., Bhattacharya 1985, Hannach and Santelices 1985, Lazo et al. 1989, Shaughnessy and De Wreede 1991, Scrosati et al. 1994, Dyck and De Wreede 1995, Lindgren and Åberg 1996, Scrosati and DeWreede 1999, OtaÏza et al. 2001, Mudge and Scrosati 2003, Scrosati and Mudge 2004 a , 2004 b , Bellgrove and Aoki 2008, McLachlan et al. 2011). This methodology has proven to be equally as effective at identifying life history phase as Fourier transform infrared spectroscopy (Brown et al. 2004), and more reliable than the iridescence criterion described by Fournet et al. (1993).
Here we present an empirical study of life history phase variation over wide temporal and spatial scales in Nova Scotia. Our objective was to determine if environmental factors could be resolved as causal agents in determining the relative abundance of gametophytic and sporophytic thalli. Several previous studies suggested that wave exposure, salinity or water depth could influence relative dominance in the life history phase of C. crispus (e.g., Craigie and Pringle 1978, Lindgren and Åberg 1996, Guidone and Grace 2010). Here we evaluate these hypotheses in the context of new data from Nova Scotia and an analysis of previous accounts.
#Dedicated to the memory of Jack L. McLachlan – friend and mentor
Populations of C. crispus ( Fig. 1 ) were collected from around Nova Scotia at various times from 1993 to 2011 and at spatial scales from 10 m to over 500 km ( Table 1 ). At most sites and times 100-150 single fronds were haphazardly collected from separate thalli at least 10 cm apart. On return to the laboratory small pieces of each frond were removed, allowed to dry on paper towels and stored at room temperature.
As a test of reproducibility of results from a given site / collection, two separate analyses were carried out. In the 62first, two collections of 100 fronds were processed from an aquaculture facility (Scotian Halibut Ltd., Woods Harbour, shelburne Co.) based on fronds originally isolated from an apparently asexual population in Basin Head, Prince Edward Island (Sharp et al. 2010), and grown in mass culture for two years. These fronds have only ever produced cystocarps and the two analyses separated by eight months showed 99 and 100% gametophytes. The single frond segment not conclusively a gametophyte gave an ambiguous result and was scored accordingly. In a second experiment, two independent lots of 100 fronds were processed from a larger collection of fronds from Tor Bay collected in October 1996. These samples gave 83% and 89% gametophytes, values not significantly different from each other ( χ 2 at p < 0.05). In addition to our own populations, published percentages of life history phases from previous analyses in eastern Canada and elsewhere were also evaluated to resolve whether or not particular environmental variables could be implicated as causal factors to explain the variation in abundance of life history phase.
Life history phases of fronds of C. crispus were determined based on the resorcinol method as described previously (Dyck et al. 1985, Garbary and De Wreede 1988). This is a simple chemical test in which a small piece of dried thallus (about 10 mg) is heated at 85-90°C in the presence of 1-1.5 mL of resorcinol-acetal reagent prepared according to Craigie and Leigh (1978) and Garbary and De Wreede (1988). Samples were processed in groups of 10, with additional frond pieces of known life history phase run as controls. Results from each population were expressed as percent gametophytic fronds.
The mean percent gametophytes of the 30 populations processed was determined along with the 95% confidence interval. A series of single sample t-tests (Zar 1999) showed that this value (76.4 ± 5.2, mean ± 95% confidence interval) was significantly greater than 70 (p < 0.05). Accordingly, we ignored the question of which life history phase was dominant in a given population, as it was patently the case that gametophytes dominated these Nova Scotia populations. The evaluation of our data in combination with previously published data was to look for patterns of differential gametophyte dominance that could be related to particular environmental gradients, i.e., wave exposure, salinity and water depth. Furthermore, if environmental factors were the primary cause of different life history ratios, then we would predict that the ratios of gametophytic to sporophytic thalli would remain relatively constant at a given site. This was done at five sites, with four of these consisting of collec-
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Chondrus crispus Stackhouse from Tor Bay Nova Scotia. (A & B) Large and small fronds. (C & D) Enlarged portions of reproductive fronds with cystocarps and tetrasporangial sori; (D) with tetrasporangial sori before (small arrow) and after (large arrow) spore release. Scale bars represent: 1 cm.
tions from three different years and time spans of two to 20 years.
To determine if different environmental variables affected the relative abundance of gametophytes, we selected relevant populations from our data set along with previously published accounts. We then evaluated the extent to which differences in ratios were present along gradients of salinity, wave exposure, and depth. To evaluate hypotheses that gradients of abundance were present, we conducted a series of χ2 analyses (Zar 1999) to determine whether differences in percentages from different pairs or groups of populations representing different ranges of a gradient were significant. In these tests, the value of one population was used as the predicted value and tested whether the other proportion was significantly different (at p < 0.05). In the temporal analysis where more than two populations were examined, the Bonferroni correction was used to avoid Type I error (Quinn and Keough 2002).
The 30 populations from six counties of Nova Scotia collected over a 20-year period from diverse habitats showed extensive variation in the ratio of gametophytic to tetrasporophytic fronds. While the mean was 77% gametophytic fronds (with 95% confidence intervals ± 5%), most samples had 67-89% gametophytic fronds ( Table 1 ). Only three populations were below 60% gametophytes, and none of the collections showed a dominance of tetrasporophytes. Thus most of the samples ranged from a ratio of about 2 : 1 to 9 : 1 (gametophytes : sporophytes). Use of χ2 statistic to compare pairs of values showed that differences of 10% were sufficient to show significance at p < 0.05.
The lowest value of 50% gametophytic fronds was found twice. One site was a wave exposed shore at Charlesville (September 2010). These fronds were collected near the upper limits of their distribution on the shore from beneath a canopy of Ascophyllum nodosum . This collection with its low sample size (n = 50) may not
Collection details for populations of Chondrus crispus from Nova Scotia analyzed for life history phase using the resorcinol-acetalNote: all habitats are fully marine, except for estuarine sites in Antigonish Harbour Habitats are characterized on a subjective wave exposure scale: very protected, protected, moderate, exposed. Tor Bay (A) and (B) separated by 1 km.
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Collection details for populations of Chondrus crispus from Nova Scotia analyzed for life history phase using the resorcinol-acetal Note: all habitats are fully marine, except for estuarine sites in Antigonish Harbour Habitats are characterized on a subjective wave exposure scale: very protected, protected, moderate, exposed. Tor Bay (A) and (B) separated by 1 km.
be representative of the general community at Charlesville as evidenced by a collection seven months previous (i.e., February 2010) taken from the drift that gave 74% gametophytes ( Table 1 ). The second collection of 50% gametophytes came from an estuarine site in Antigonish Harbour; this population was significantly lower than two other collections from the same site taken in different years (i.e., 67%, 81%).
Another low value for gametophyte dominance (i.e., 58%) came from near Captains Island, in Antigonish Harbour. This is an estuarine site adjacent to the main channel through the harbour. The C. crispus is permanently submerged and grows on rocks in a bed of Zostera marina. Here, thalli are challenged by strong currents, low wave action and occasional periods when the salinity can drop to 10 psu or less. Ice scour during spring break up would be a major stress on this population. Two other populations from nearby areas in Antigonish Harbour grew on shallow subtidal rocks and gave higher values (i.e., 64%, 89%). The remaining samples in Antigonish Harbour (all at Seabright) are extremely protected from wave exposure, and their location further up the estuary would give greater exposure to low salinities (i.e., <10 psu during spring runoff and following heavy rains). The three values for this site at 50%, 67% and 81% gametophytes were all significantly different from each other (p < 0.05), and the high value also differs from the Captains Island sample ( Table. 1 & 2 ).
The possibility that estuarine, or low salinity conditions might influence gametophyte:sporophyte ratios was examined by taking all of our samples from Antigonish Harbour where salinities can vary from 0-28 psu and combining these with the values from low salinity samples in the literature ( Table 2 ). These nine values were then compared with the overall mean from our complete data set of 30 samples. The mean of the low salinity sites was 68 ± 12% (mean ± standard deviation). A t-test showed no significant difference between these populations and the overall mean in our entire analysis. A further attempt
Percentage of gametophytic thalli of Chondrus crispus in low salinity conditions with values from current study or extremes of gradients from previously published accounts
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Percentage of gametophytic thalli of Chondrus crispus in low salinity conditions with values from current study or extremes of gradients from previously published accounts
to resolve a salinity gradient within Antigonish Harbour, performed by separating populations from the more saline outer harbour (58%, 64%, 89% gametophytes) from the more brackish inner harbour (50%, 67%, 81% gametophytes), showed no apparent trend with salinity.
The possibility that life history phase was modified by wave exposure was examined in three sets of populations from Tor Bay, the Bay of Fundy and in Antigonish Harbour ( Table 3 ). Within each region the pairs of populations (wave protected vs. wave exposed) were collected in the same season. At Tor Bay where the two populations were selected along the wave exposure gradient of Heaven and Scrosati (2008), the protected site had fewer gametophytes (significant at p < 0.05) whereas the difference in values from the other sites was not significant.
The most intensively sampled location temporally (i.e., 1996-2011), spatially (ca. 1 km) and ecologically (i.e., wave protected to wave exposed, rock pools to low intertidal and drift) was at Tor Bay, a fully marine area on the Atlantic coast. Values ranged from 64 to 89% gametophytes for attached populations, and two drift collections had values of 85% and 96% gametophytes ( Table 1 ). Additional samples from Tor Bay by Scrosati et al. (1994) and Scrosati and Mudge (2004 a ) extended the temporal sampling to 1991 and provided an additional intermediate sample from 2003 ( Table 4 ). Even excluding the high intertidal rock pool population (89% gametophytes) and the two drift collections (85% and 96% gametophytes), temporal sampling and populations collected over a wave exposure gradient showed significant differences. Thus, the remaining collections had a strong dominance of gametophytic thalli with the lowest value (64%) not significantly different from 2 : 1 (gametophytes : sporophytes).
Other sites (Drumhead, Charlesville) along the Atlantic coast of Nova Scotia showed a similar pattern of strong gametophytic dominance as well as significant differences in the proportions of gametophytes among collections. The two collections from Drumhead (70% and 97% gametophytes) are consistent with other values from the Atlantic coast of Nova Scotia by Bhattacharya (1984) (90-93% gametophytes) and McLachlan et al. (2011) (58-92% gametophytes).
Our collections from fully marine sites in the Bay of Fundy showed variation from 63-90% gametophytes, i.e., ca. 2 : 1 to 9 : 1. Significant differences occurred with small spatial separation (i.e., east and west sides of Gullivers Cove, 80% and 68% gametophytes, respectively) and with temporal sampling over one year (63 to 83% gametophytes).
Gametophytic thalli clearly dominate in Nova Scotian populations of C. crispus . While individual populations and sites in Nova Scotia may have near equality of phases or tetrasporophyte dominance (e.g., Craigie and Pringle 1978), these are clearly exceptions. Thus, means of multiple populations from our study across ranges of environments gave values of 66-76% gametophytes. Furthermore, many sites in the literature show ≻90% gametophytes (e.g., Bhattacharya 1984, 1985). A simple explanation for the dominance of gametophytes over tetrasporophytes derives from the fact that C. crispus forms both male and female thalli. Since only the female and tetrasporophytic thalli produce spores (i.e., cystocarps and tetrasporangial sori, Fig. 1 ), and since some of the gametophytes would be expected to be males (Chen and McLachlan 1972, Taylor and Chen 1973), then a ratio of 2 : 1 (gametophyte : sporophyte) could be expected if males and females occurred in equal numbers (but see Mathie-
Percent gametophytes at selected sites in our data that represent a wave exposure gradientSee Table 1 for details on population numbers. n.s.: not significant. **Significant at p < 0.05.
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Percent gametophytes at selected sites in our data that represent a wave exposure gradient See Table 1 for details on population numbers. n.s.: not significant. **Significant at p < 0.05.
son and Prince 1973). The underlying assumption here is that female gametophytes (i.e., carpospore producing) and tetrasporophytes have equivalent fecundities. This assumption is consistent with results of Bhattacharya (1984, 1985) and Ferná ndez and Menéndez (1991). Given the similarities in size and shape of cystocarpic and tetrasporophytic fronds, and the apparent absence of biomechanical properties leading to selective frond removal that might be associated with carrageenan differentiation in C. crispus (Carrington et al. 2001), gametophytic dominance of 2 : 1 would be an expected ratio. The biomechanical properties of life history phases in Gigartinaceae cannot be entirely excluded as a potential explanation, as they were correlated with distributions of Mazzaella spp. (Shaughnessy et al. 1996, Mach 2009) and C. verrucosus (Bellgrove personal communication). Regardless, we did not find any association between wave exposure and phase ratios in C. crispus .
Developing a realistic model that explains life history demography of C. crispus is problematic. We have limited data on the fecundity of tetrasporophytic and cystocarpic thalli. Also lacking are factors that might differentially affect tetraspore and carpospore viability on a seasonal basis and their subsequent survival as they interact with each other, and in a complex biotic and abiotic environment. These factors were emphasized in theoretical models developed by Scrosati and DeWreede (1999), Fierst et al. (2005) and Thornber and Gaines (2003, 2004). There have been attempts to deal with these issues specifically in C. crispus from Nova Scotia and northern Spain (Bhattacharya 1984, 1985, Fernandez and Menéndez 1991, Scrosati et al. 1994). The latter concluded that spore production in the two phases was roughly equivalent (8 × 10 10 m -2 y -1 ), and Bhattacharya (1984) concluded with Nova Scotia populations that “the numerical dominance of haploid fronds was established during the initial stages of sporeling growth.” Nonetheless, a culture study by Scrosati et al. (1994) found that tetraspores were more viable than carpospores, and Lindgren and Åberg (1996) found greater incidence of reproductive structures on tetrasporophytic plants than on gametophytes.
Populations collected from the drift high in gametophytes may be explained by the tendency of gametophytic plants to degenerate more readily than tetrasporophytes. Bhattacharya (1984) found survivorship of tetrasporophytes to be greater than cystocarpic plants observed simultaneously. A population of C. crispus occurring at Basin Head, Prince Edward Island, Canada is more than 99% gametophytic, reproducing vegetatively (Sharp et al. 2010).
Two other studies of C. crispus were conducted at Tor Bay approximately 1 km east of the current concentration of sampling sites. Scrosati et al. (1994) found 72-78% gametophytes in three monthly samples in 1991. Resampling of the same area in 2003 gave 62% gametophytes (Scrosati and Mudge 2004b). The first set of samples fall within the mean and 95% confidence interval for all our analyses. χ2 analysis demonstrates that the 2003 collection is significantly different from the average of the 1991 population. The intervening period between 1991 and 2003 had at least two major environmental disturbances from pack ice and a severe fall storm. The former removed much of the vegetation in the lower intertidal zone, whereas the latter destroyed a seashore boardwalk and carried major pieces at least 100 m into spruce forest (Garbary, unpublished observations). Resampling of the same site in 2011 (population 1, Table 1 ) showed that the site had returned to the original values from 1991.
Wave exposure has been implicated as a regulatory mechanism for abundance of life history phases in Mazzaella species (Mudge and Scrosati 2003, Scrosati and Mudge 2004 a ). Two of our samples at Tor Bay (samples 3 & 5, Table 1 ) were specifically chosen to represent the extremes of the wave exposure gradient defined by Heaven and Scrosati (2008). These two samples yielded 69% and 76% gametophytes (i.e., from 2 : 1 to 3 : 1, not significant at p ≺ 0.05) for the protected and exposed samples, respectively, and are nowhere near the extremes represented in our data and in the literature (i.e., almost 1 : 1 to ≻9 : 1). Table 3 summarizes our data on wave exposure and life history phase in C. crispus , and we did not recover any consistent trend.
The possibility that there might be a depth gradient for abundance of gametophytic thalli in Irish moss was proposed by Craigie and Pringle (1978). While they found an increase in tetrasporophytes with depth in Nova Scotia and Prince Edward Island, more comprehensive sampling by Lazo et al. (1989) did not uncover this pattern. This pattern was also not apparent in the subtidal sampling of Chopin et al. (1988), who found an increase in tetrasporophytes in a bed of C. crispus that had been dragraked. Bhattacharya (1984) also found extremely high gametophyte abundance (i.e., ≻90%) in both subtidal and intertidal samples much like a similar sampling by Wright (1981; not seen, cited by Bhattacharya 1984).
Given that conspicuous gametophyte dominance is the rule in C. crispus (i.e., 2 : 1 or greater), how can we account for those samples in which the ratio is skewed towards 1 : 1 or has a dominance of tetrasporophytes as in Lazo et al. (1989)? We suggest two mechanisms: one based on occasional catastrophic loss of localized populations, and the second based gradual spread at the periphery of established populations. Catastrophic loss might occur from storm damage or major ice abrasion. The bulk of the remaining thalli will be gametophytic; hence the potential spore rain will be largely comprised of carpospores that will produce tetrasporophytic thalli. The sporadic nature of the tetrasporophyte dominated samples (e.g., Craigie and Pringle 1978, Lazo et al. 1989, Guidone and Grace 2010) may be accounted for by stochastic events that created new space for colonization. This was also suggested by Lindgren and Åberg (1996), and demonstrated experimentally by Bhattacharya (1984) who cleared space in the upper part of the C. crispus zone with a high proportion of gametophytes (95%); this space was recolonized by a population with a much lower proportion of gametophytes (63%).
Our explanation is consistent with the conclusion of Lazo et al. (1989) and McLachlan et al. (2011) to account for the near equality and occasional predominance of tetrasporophytes in Prince Edward Island. Here new space for colonization is being produced because the sandstone is so friable and whole thalli are being removed along with the underlying substratum. Parker and McLachlan (1990) also showed that large proportions of the C. crispus population are epiphytic on the crustose coralline Phymatolithon, that may also shed whole cell layers along with the epiphytic Irish moss.
A second mechanism that could be responsible for tetrasporophyte dominance involves the periphery of a population that is undergoing gradual spread. Such spread might be a consequence of environmental change (e.g., climate change or competitive interactions). In such situations the marginal sites would have a greater spore rain of carpospores from the gametophyte dominated population as in Bellgrove and Aoki (2008). This could account for the tetrasporophyte dominated populations at the deeper edges of beds in Prince Edward Island (Craigie and Pringle 1978). It could also explain the 50% gametophytes from the September 2010 population at Charlesville. This population was collected from the upper margin of the C. crispus zone when fronds were difficult to reach because an incoming tide precluded collection from the lower part of the C. crispus zone. Sea level rise on gradually sloping shores could theoretically produce the necessary new habitat for colonization.
Over time, we suggest that, barring a high frequency of catastrophic events, that populations that were initially tetrasporophyte dominated, would subsequently return to the 2 : 1 (or higher) ratio that characterizes most populations. In light of the inability to relate relative abundance of a life history stage of C. crispus to environmental gradients of depth, salinity or wave exposure, we suggest that such adaptive gradients do not exist, and that a dominance of gametophytes (2 : 1 or higher) represents the equilibrium for this species. Furthermore, we suggest that studies of C. crispus or other species using populations from only a few sites risk recovering purely stochastic differences that do not test the adaptive significance of life history phase to the very real environmental
Percentage gametophytes at sites where populations were evaluated at different times (T) over at least a two-year periodSee Table 1 for details of site locations. Significant differences based onχ2tests at p ≺ 0.05.aScrosati et al. 1994.bScrosati and Mudge 2004b.
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Percentage gametophytes at sites where populations were evaluated at different times (T) over at least a two-year period See Table 1 for details of site locations. Significant differences based on χ2 tests at p ≺ 0.05. aScrosati et al. 1994. bScrosati and Mudge 2004b.
gradients to which they are being related. This is consistent with the temporal variation we found in that all five sites sampled in more than one year showed significant differences among years ( Table 4 ). Our study shows that changes in periods as short as one year may lead to significant changes in the proportion of life history phases, and that these changes may be greater in extent than differences associated with environmental gradients.
We suggest a series of environmental and biotic factors that might account for these stochastic changes. First, storm action can severely modify the lower intertidal zone by displacing boulders into or out of the habitat or even just turning them over. Secondly, ice scour from pack ice can effectively remove a large expanse of intertidal algae. With respect to biotic factors, abundant sea urchins can effectively remove the entire flora from the subtidal zone. This will leave intertidal populations of C. crispus that may have extremely high percentages of gametophytes (i.e., 90% or more) that will recolonize tetrasporophytes. A second biotic factor that may contribute to dominance of gametophytes in C. crispus is the differential impact of green algal endophytes that have greater negative effects on tetrasporophytic thalli (Correa and McLachlan 1992). While these are independent processes, they may function synergistically to create the gametophyte dominance that is apparent in Nova Scotia.
We thank L. Beveridge, A. Flynn, J. Garbary, A. Miller and K. Zefkic for assisting with sample collection, and M. Garbary provided helpful comments on an earlier draft. R. Scrosati and B. Taylor provided statistical advice and A. Bellgrove gave valuable comments during review. This work was supported by grants from the Natural Sciences and Engineering Research Council of Canada and the University Council for Research of St. Francis Xavier University to DJG.
Bellgrove A , Aoki M. N 2008 Variation in gametophyte dominance in populations ofChondrus verrucosus(Gigartinaceae Rhodophyta) Phycol. Res 56 246 - 254    DOI : 10.1111/j.1440-1835.2008.00506.x
Bhattacharya D 1984 The demography ofChondrus crispusStackhouse Dalhousie University Halifax NS Canada 120 -
Bhattacharya D 1985 The demography of fronds ofChondrus crispusStackhouse J. Exp. Mar. Biol. Ecol 91 217 - 231    DOI : 10.1016/0022-0981(85)90177-7
Bird C. J , McLachlan J. L 1992 Seaweed flora of the maritimes. 1. Rhodophyta the red algae Biopress Bristol 177 -
Bird C. J , van der Meer J.P 1993 Systematics of economically important marine algae: a Canadian perspective Can. J. Bot 71 361 - 369
Brown M. T , Neish A , Harwood D 2004 Comparison of three techniques for identifying isomorphic phases ofChondrus crispus(Gigartinaceae) J. Appl. Phycol 16 447 - 450    DOI : 10.1007/s10811-004-5507-y
Carrington E , Grace S. P , Chopin T 2001 Life history phases and the biomechanical properties of the red algaChondrus crispus(Rhodophyta) J. Phycol 37 699 - 704    DOI : 10.1046/j.1529-8817.2001.00169.x
Chen L. C. -M , McLachlan J 1972 The life history ofChondrus crispusin culture Can. J. Bot 50 1055 - 1060    DOI : 10.1139/b72-129
Chen L. C. -M , McLachlan J , Neish A. C , Shacklock P.F 1973 The ratio of kappa- to lambda-carrageenan in nuclear phases of the rhodophycean algaeChondrus crispusandGigartina stellata J. Mar. Biol. Assoc. U. K 53 11 - 16    DOI : 10.1017/S0025315400056599
Chopin T 1986 The red algaChondrus crispusStackhouse (Irish moss) and carrageenans: a review Can. Tech. Rep. Fish. Aquat. Sci 1514 1 - 69
Chopin T , Pringle J. D , Semple R. E 1988 Reproductive capacity of dragraked and non-dragraked Irish moss (Chondrus crispusStackhouse) beds in the southern Gulf of St. Lawrence Can. J. Fish. Aquat. Sci 45 758 - 766    DOI : 10.1139/f88-093
Correa J. A , McLachlan J. L 1992 Endophytic algae ofChondrus crispus(Rhodophyta). IV. Effects on the host following infections byAcrochaete operculataandA. heteroclada(Chlorophyta) Mar. Ecol. Prog. Ser 81 73 - 87    DOI : 10.3354/meps081073
Craigie J. S , Leigh C , Hellebust J. A , Craigie J. S 1978 Carrageenans and agars.In Handbook of Phycological Methods: Physiological and Biochemical Methods Cambridge University Press Cambridge 109 - 131
Craigie J. S , Pringle J. D 1978 Spatial distribution of tetrasporophytes and gametophytes in four maritime populations ofChondrus crispus Can. J. Bot 56 2910 - 2914    DOI : 10.1139/b78-349
Dyck L , De Wreede R. E , Garbary D 1985 Life history phases inIridaea cordata(Gigartinaceae): relative abundance and distribution from British Colombia to California Jpn. J. Phycol 33 225 - 232
Dyck L. J , De Wreede R. E 1995 Patterns of seasonal demographic change in the alternate isomorphic stages ofMazzaella splendens(Gigartinales Rhodophyta) Phycologia 34 390 - 395    DOI : 10.2216/i0031-8884-34-5-390.1
Fernández C , Menéndez M. P 1991 Ecology ofChondrus crispusStackhouse on the northern coast of Spain. II. Reproduction Bot. Mar 34 303 - 310    DOI : 10.1515/botm.1991.34.4.303
Fierst J , TerHorst C , Kübler J. E , Dudgeon S 2005 Fertilization success can drive patterns of phase dominance in complex life histories. J. Phycol 41 238 - 249    DOI : 10.1111/j.1529-8817.2005.04024.x
Fournet I , Deslandes E , Floc’h J. -Y 1993 Iridescence: a useful criterion to sort gametophytes from sporophytes in the red algaChondrus crispus J. Appl. Phycol 5 535 - 537    DOI : 10.1007/BF02182512
Garbary D. J , De Wreede R. E , Lobban C. S , Chapman D. J , Kremer B. P 1988 Life history phases in natural populations of Gigartinaceae (Rhodophyta): quantification using resorcinol.In Experimental Phycology: A Laboratory Manual Cambridge University Press Cambridge MA 174 - 178
Guidone M , Grace S 2010 The ratio of gametophytes to tetrasporophytes of intertidalChondrus crispus(Gigartinaceae) across a salinity gradient Rhodora 112 80 - 84    DOI : 10.3119/08-35.1
Hannach G , Santelices B 1985 Ecological differences between the isomorphic reproductive phases of two species ofIridaea(Rhodophyta: Gigartinales) Mar. Ecol. Prog. Ser 22 291 - 303    DOI : 10.3354/meps022291
Heaven C. S , Scrosati R. A 2008 Benthic community composition across gradients of intertidal elevation wave exposure and ice scour in Atlantic Canada Mar. Ecol. Prog. Ser 369 13 - 23    DOI : 10.3354/meps07655
Lazo M. L , Greenwell M , McLachlan J 1989 Population structure ofChondrus crispusStackhouse (Gigartinaceae Rhodophyta) along the coast of Prince Edward Island Canada: distribution of gametophytic and sporophytic fronds J. Exp. Mar. Biol. Ecol 126 45 - 58    DOI : 10.1016/0022-0981(89)90123-8
Lindgren A , Åberg P 1996 Proportion of life cycle stages ofChondrus crispusand its population structure: a comparison between a marine and an estuarine environment Bot. Mar 39 263 - 268    DOI : 10.1515/botm.1996.39.1-6.263
MacFarlane C 1952 A survey of certain seaweeds of commercial importance in southwest Nova Scotia Can. J. Bot 30 78 - 97    DOI : 10.1139/b52-008
Mach K. J 2009 Mechanical and biological consequences of repetitive loading: crack initiation and fatigue failure in the red macroalgaMazzaella J. Exp. Biol 212 961 - 976    DOI : 10.1242/jeb.026989
Mathieson A. C , Burns R. L 1975 Ecological studies of economic red algae. V. Growth and reproduction of natural and harvested populations ofChondrus crispusStackhouse in New Hampshire J. Exp. Mar. Biol. Ecol 17 137 - 156    DOI : 10.1016/0022-0981(75)90027-1
Mathieson A. C , Prince J. S 1973 Ecology ofChondrus crispusStackhouse Proc. N. S. Inst. Sci 27 (Suppl) 53 - 79
McCandless E. L 1981 Biological control of carrageenan structure: effects conferred by the phase of life cycle of the carrageenophyte Proc. Int. Seaweed Symp 8 1 - 18
McCandless E. L , Craigie J. S , Walter J. A 1973 Carrageenans in the gametophytic and sporophytic stages ofChondrus crispus Planta 112 201 - 212    DOI : 10.1007/BF00385324
McLachlan J , Mauchline J , Nemoto T 1991 Chondrus crispus (Irish moss) an ecologically important and commercially valuable species of red seaweed of the North Atlantic Ocean.In Marine Biology: Its Accomplishment and Future Prospect Hokusensha Publishing Co Tokyo 217 - 233
McLachlan J , Greenwell M , Bird C. J , Holmsgaard J. E 1987 Standing stocks of seaweeds of commercial importance on the north shore of Prince Edward Island Canada Bot. Mar 30 277 - 289    DOI : 10.1515/botm.1987.30.4.277
McLachlan J. L , Blanchard W , Field C , Lewis N. I 2011 Gametophyte life-history dominance ofChondrus crispus(Gigartinaceae Rhodophyta) along the Atlantic coast of Nova Scotia Canada Algae 26 51 - 60
McLachlan J. L , Quinn J , MacDougall C 1989 The structure of the plant ofChondrus crispusStackhouse (Irish moss) J. Appl. Phycol 1 311 - 317    DOI : 10.1007/BF00003467
Mudge B , Scrosati R 2003 Effects of wave exposure on the proportion of gametophytes and tetrasporophytes ofMazzaella oregona(Rhodophyta: Gigartinales) from Pacific Canada J. Mar. Biol. Assoc. U. K 83 701 - 704    DOI : 10.1017/S0025315403007665h
Otaíza R. D , Abades S. R , Brante A. J 2001 Seasonal changes in abundance and shifts in dominance of life history stages of the carrageenophyteSarcothalia crispata(Rhodophyta Gigartinales) in south-central Chile J. Appl. Phycol 13 161 - 171    DOI : 10.1023/A:1011135308283
Parker T , McLachlan J 1990 Relationship between cover ofChondrus crispus(Gigartinales Rhodophyta) andPhymatolithon(Corallinales Rhodophyta) on friable rock substrata Hydrobiologia 204/205 247 - 251
Quinn G. P , Keough M. J 2002 Experimental design and data analysis for biologists Cambridge University Press Cambridge 537 -
Scrosati R , DeWreede R. E 1999 Demographic models to simulate the stable ratio between ecologically similar gametophytes and tetrasporophytes in populations of the Gigartinaceae (Rhodophyta) Phycol. Res 47 153 - 157    DOI : 10.1111/j.1440-1835.1999.tb00295.x
Scrosati R , Garbary D. J , McLachlan J 1994 Reproductive ecology ofChondrus crispus(Rhodophyta Gigartinales) from Nova Scotia Canada. Bot. Mar 37 293 - 300    DOI : 10.1515/botm.1994.37.4.293
Scrosati R , Mudge B 2004a Effects of elevation wave exposure and year on the proportion of gametophytes and tetrasporophytes inMazzaella parksii(Rhodophyta Gigartinaceae) populations Hydrobiologia 520 199 - 205    DOI : 10.1023/B:HYDR.0000027839.48584.6c
Scrosati R , Mudge B 2004b Persistence of gametophyte predominance inChondrus crispus(Rhodophyta Gigartinaceae) from Nova Scotia after 12 years Hydrobiologia 519 215 - 218    DOI : 10.1023/B:HYDR.0000026600.88646.31
Sharp G. J 1987 Growth and reproduction in wild and cultivated stocks ofChondrus crispus Hydrobiologia 151/152 349 - 354
Sharp G , Semple R , Vandermeulen H , Wilson M , LaRocque C , Nebel S 2010 The Basin Head Irish moss (Chondrus crispus) population abundance and distribution 1980 to 2008. Research document No. 2010/054 DFO Canadian Science Advisory Secretariat Dartmouth NS 32 -
Shaughnessy F. J , De Wreede R. E 1991 Reliability of the resorcinol method for identifying isomorphic phases in the Gigartinaceae (Rhodophyta) J. Appl. Phycol 3 121 - 127    DOI : 10.1007/BF00003694
Shaughnessy F. J , De Wreede R. E , Bell E. C 1996 Consequences of morphology and tissue strength to blade survivorship of two closely related Rhodophyta species Mar. Ecol. Prog. Ser 136 257 - 266.    DOI : 10.3354/meps136257
Taylor A. R. A , Chen L. C. -M 1973 The biology ofChondrus crispusStackhouse: systematics morphology and life history Proc. N. S. Inst. Sci 27 (Suppl) 1 - 21
Taylor W. R 1962 Marine algae of the northeastern coast of North America Revised ed University of Michigan Press Ann Arbor MI 509 -
Thornber C. S , Gaines S. D 2003 Spatial and temporal variation of haploids and diploids in populations of four congeners of the marine algaMazzaella Mar. Ecol. Prog. Ser 258 65 - 77    DOI : 10.3354/meps258065
Thornber C. S , Gaines S. D 2004 Population demographics in species with biphasic life cycles Ecology 85 1661 - 1674    DOI : 10.1890/02-4101
Wright E. C 1981 The distribution and morphological variation of the tetrasporophytic phase and the gametophytic phase of the isomorphic algaChondrus crispusStackhouse Dalhousie University Halifax NS Canada 21 -
Yaphe W , Arsenault G. P 1965 Improved resorcinol reagent for determination of fructose and 36-anhydrogalactose in polysaccharides Anal. Biochem 13 143 - 148    DOI : 10.1016/0003-2697(65)90128-4
Zar J. H 1999 Biostatistical analysis 4th ed Prentice Hall Upper Saddle River NJ 663 -