Abstract:This is an open access article under the terms of the Creative Commons Attribution License, which permits use, distribution and reproduction in any medium, provided the original work is properly cited.
“…A recent genomic assessment over the entire distribution of eelgrass, in both the Pacific and Atlantic, only detected a small percentage of clonemates (9%; Yu et al, 2023), as well as previous genetic assessments, based on microsatellites, along the Kattegat, Skagerrak and Southern Baltic Sea (Jahnke et al, 2018(Jahnke et al, , 2020Martínez-García et al, 2021). A high incidence of clonality in the Baltic Sea has previously been shown in other species (e.g., macroalgae; Bergström et al, 2003;Johannesson and André, 2006;Pereyra et al, 2023). A potential explanation for the high incidence of clonality in multiple facultative sexual species in the Baltic Sea is that under extreme conditions, environmental factors may be unsuitable for one or several stages of sexual reproduction.…”
Section: Clonalitysupporting
confidence: 53%
“…Indeed, although flowering eelgrass and seed germination have been observed at as low as 5 psu in the Baltic Sea (Boström, 1995;Salo, 2014;Salo et al, 2014), this salinity level might be too low for successful seed ripening or seedling establishment. In such a scenario, clonality might increase survival in these extreme environments (Edgeloe et al, 2022), and be especially competitive during colonization and range expansions into such environments (Rafajlović et al, 2017;Pereyra et al, 2023). Indeed, the Baltic Sea turned marine only recently (∼8,000 years ago) and has been colonized since then by marine species such as eelgrass (Snoeijs-Leijonmalm et al, 2017).…”
Section: Clonalitymentioning
confidence: 99%
“…Moreover, flowering shoots are rarely seen in the northern part of the Baltic Sea (Boström, 1995;Möller and Martin, 2007). Clonality may be advantageous when colonizing a new area and during range expansions (Rafajlović et al, 2017;Pereyra et al, 2023) and might favor survival in extreme environments (Edgeloe et al, 2022), but in terms of conservation a high dominance of clonal reproduction is generally seen as a disadvantage, particularly under global change (Pipithkul et al, 2021). Nevertheless, some ancient clones have persisted for centuries to millennia, and due to their presumed high fitness in the local environment are referred to as all-purpose-genotypes.…”
Zostera marina (eelgrass) is a foundation species in coastal zones in the northern hemisphere. Eelgrass is declining across its distribution, a trend likely to accelerate under climate change. In Sweden, eelgrass is a species of particular concern in management and conservation. Here, we provide information on genetic variation, an important component for the potential persistence and adaptation of any species in a changing environment. In particular, the steep salinity gradient over which eelgrass is distributed along the Swedish coast (26 psu on the west coast to 5 psu on the east coast) calls for a better understanding of genetic diversity, connectivity, and potential for local adaptation. To assess genetic variation and population genetic structure, we genotyped individuals with 2,138 single nucleotide polymorphisms (SNPs) from 15 eelgrass meadows spanning the whole Swedish distribution. We found a geographic population genetic structure from west to east parallel to the salinity gradient and with a clear genetic break at the entrance to the Baltic Sea. Meadows along the low salinity east coast consisted of a few or only one clone. Eelgrass on the west coast had higher genotypic richness, higher genetic variation, and showed population differentiation on smaller geographic scales. With their low genetic variation, the east coast meadows are especially threatened amidst global changes. Lack of sexual reproduction and the capacity to generate new genotypes is an issue that needs to be seriously considered in management and conservation. In addition, the lack of sexual reproduction renders clonal eelgrass less likely to recover and recolonize after disturbance, and more challenging to restore. The here provided information on genetic clusters, clonality, and genetic variation can be included for prioritizing meadows for conservation and for identifying meadows for restoration purposes. Most importantly, genetic monitoring is urgently needed to assess temporal genetic changes of eelgrass along the Swedish coast and elsewhere facing climate change.
“…A recent genomic assessment over the entire distribution of eelgrass, in both the Pacific and Atlantic, only detected a small percentage of clonemates (9%; Yu et al, 2023), as well as previous genetic assessments, based on microsatellites, along the Kattegat, Skagerrak and Southern Baltic Sea (Jahnke et al, 2018(Jahnke et al, , 2020Martínez-García et al, 2021). A high incidence of clonality in the Baltic Sea has previously been shown in other species (e.g., macroalgae; Bergström et al, 2003;Johannesson and André, 2006;Pereyra et al, 2023). A potential explanation for the high incidence of clonality in multiple facultative sexual species in the Baltic Sea is that under extreme conditions, environmental factors may be unsuitable for one or several stages of sexual reproduction.…”
Section: Clonalitysupporting
confidence: 53%
“…Indeed, although flowering eelgrass and seed germination have been observed at as low as 5 psu in the Baltic Sea (Boström, 1995;Salo, 2014;Salo et al, 2014), this salinity level might be too low for successful seed ripening or seedling establishment. In such a scenario, clonality might increase survival in these extreme environments (Edgeloe et al, 2022), and be especially competitive during colonization and range expansions into such environments (Rafajlović et al, 2017;Pereyra et al, 2023). Indeed, the Baltic Sea turned marine only recently (∼8,000 years ago) and has been colonized since then by marine species such as eelgrass (Snoeijs-Leijonmalm et al, 2017).…”
Section: Clonalitymentioning
confidence: 99%
“…Moreover, flowering shoots are rarely seen in the northern part of the Baltic Sea (Boström, 1995;Möller and Martin, 2007). Clonality may be advantageous when colonizing a new area and during range expansions (Rafajlović et al, 2017;Pereyra et al, 2023) and might favor survival in extreme environments (Edgeloe et al, 2022), but in terms of conservation a high dominance of clonal reproduction is generally seen as a disadvantage, particularly under global change (Pipithkul et al, 2021). Nevertheless, some ancient clones have persisted for centuries to millennia, and due to their presumed high fitness in the local environment are referred to as all-purpose-genotypes.…”
Zostera marina (eelgrass) is a foundation species in coastal zones in the northern hemisphere. Eelgrass is declining across its distribution, a trend likely to accelerate under climate change. In Sweden, eelgrass is a species of particular concern in management and conservation. Here, we provide information on genetic variation, an important component for the potential persistence and adaptation of any species in a changing environment. In particular, the steep salinity gradient over which eelgrass is distributed along the Swedish coast (26 psu on the west coast to 5 psu on the east coast) calls for a better understanding of genetic diversity, connectivity, and potential for local adaptation. To assess genetic variation and population genetic structure, we genotyped individuals with 2,138 single nucleotide polymorphisms (SNPs) from 15 eelgrass meadows spanning the whole Swedish distribution. We found a geographic population genetic structure from west to east parallel to the salinity gradient and with a clear genetic break at the entrance to the Baltic Sea. Meadows along the low salinity east coast consisted of a few or only one clone. Eelgrass on the west coast had higher genotypic richness, higher genetic variation, and showed population differentiation on smaller geographic scales. With their low genetic variation, the east coast meadows are especially threatened amidst global changes. Lack of sexual reproduction and the capacity to generate new genotypes is an issue that needs to be seriously considered in management and conservation. In addition, the lack of sexual reproduction renders clonal eelgrass less likely to recover and recolonize after disturbance, and more challenging to restore. The here provided information on genetic clusters, clonality, and genetic variation can be included for prioritizing meadows for conservation and for identifying meadows for restoration purposes. Most importantly, genetic monitoring is urgently needed to assess temporal genetic changes of eelgrass along the Swedish coast and elsewhere facing climate change.
“…4d), 1 in Estonia (352 years), 2 in Norway (271 and 847 years) and 1 in Finland (1,403 years). All genets >270 years of age were located in higher latitudes (>50° N) in the North Atlantic, indicating that marginal populations were more likely to maintain old genets 4,11,36 and supporting the established geographic parthenogenesis pattern 37 . Although the evolutionary history in the Pacific is much longer than that in the Atlantic 35 , Pacific eelgrass genets were young (<40 years).…”
Section: Age Estimation Of 15 Globally Distributed Z Marina Genetsmentioning
Age and longevity are key parameters for demography and life-history evolution of organisms. In clonal species, a widespread life history among animals, plants, macroalgae and fungi, the sexually produced offspring (genet) grows indeterminately by producing iterative modules, or ramets, and so obscure their age. Here we present a novel molecular clock based on the accumulation of fixed somatic genetic variation that segregates among ramets. Using a stochastic model, we demonstrate that the accumulation of fixed somatic genetic variation will approach linearity after a lag phase, and is determined by the mitotic mutation rate, without direct dependence on asexual generation time. The lag phase decreased with lower stem cell population size, number of founder cells for the formation of new modules, and the ratio of symmetric versus asymmetric cell divisions. We calibrated the somatic genetic clock on cultivated eelgrass Zostera marina genets (4 and 17 years respectively). In a global data set of 20 eelgrass populations, genet ages were up to 1,403 years. The somatic genetic clock is applicable to any multicellular clonal species where the number of founder cells is small, opening novel research avenues to study longevity and, hence, demography and population dynamics of clonal species.
“…Often, the contribution of sexual and clonal reproduction to local population structure varies among species and localities [3][4][5] , resulting in asexual populations of ramets that are nested within the "classical" population of genets 2,6 . Coral, algae, seagrass, or poplar genets, for example, can reach considerable size and therefore age with linear extents of >1 km [7][8][9][10][11] . The apparent persistence and resilience of asexual ramet populations is astonishing in light of the considerable temporal and spatial variation they may experience over their lifetimes despite little genetic variation (but see refs 10,12 ) and raises questions about these species' adaptability in a rapidly changing climate 13 .…”
Age and longevity are key parameters for demography and life-history evolution of organisms. In clonal species, a widespread life history among animals, plants, algae and fungi, the sexually produced offspring (the genet) grows indeterminately by producing iterative modules, or ramets. The age of large genets often remains elusive, while estimates based on their spatial extent as proxy for age are unreliable. Here, we present a method for age estimation using a molecular clock based on the accumulation of fixed somatic genetic variation (SoGV) that segregates among ramets of the same genet. Using a stochastic model of a generic clonal organism, we demonstrate that the accumulation of fixed SoGV via somatic genetic drift will approach linearity after a short lag phase, and is determined by the mitotic mutation rate, without direct dependence on asexual generation time. The lag phase decreased with lower stem cell population size (N), number of founder cells for the formation of new modules (N0), and the ratio of symmetric vs. asymmetric stem cell divisions. We apply the somatic genetic clock to the clonal plant modelZostera marina(eelgrass) and show that linearity is approached within a few years. Taking advantage of two long-term cultivation experiments forZ. marina(4 and 17 years respectively) as calibration points, we find genet ages up to 1,403 years in a global data set of 20 eelgrass populations. The somatic genetic clock is applicable to any multicellular clonal species where a small number of founder cells are recruited to form new ramets, opening novel research avenues to study longevity and hence, demography and population dynamics of clonal species.
scite is a Brooklyn-based organization that helps researchers better discover and understand research articles through Smart Citations–citations that display the context of the citation and describe whether the article provides supporting or contrasting evidence. scite is used by students and researchers from around the world and is funded in part by the National Science Foundation and the National Institute on Drug Abuse of the National Institutes of Health.