spartina alterniflora loisel

Universal primers for amplification of three non-coding regions of chloroplast DNA. and the likelihood of cross pollination. doi: 10.3354/meps292111, Okoshi, K. (2007). Environ. Here, we studied the effects of invasion and ecological replacement using S. apetala on soil organic carbon fractions and stock on Qi’ao Island. Again, values of AR in S. alterniflora populations in Japan were lower than those in the U.S. and China populations, and the formation of a bottleneck was expected in Japanese populations. Mol. 90 (4), 502–503. International trade serves as one of the driving factors for the widespread invasion of the invasive species (Elton, 1958; Lockwood et al., 2007; Davis, 2009; Richardson, 2011). Invasion Biology (Oxford, UK: Oxford University Press). Plant Mol. 14 (8), 2611–2620. Distortion of allele frequency distributions provides a test for recent population bottlenecks. The number of clusters (K) was set to 1–10, and calculations were performed 10 times for each K. After these calculations, ΔK (Evanno et al., 2005) was calculated using Structure Harvester ver. (Poaceae) Introduced Unintentionally Into Japan and Its Invasion Pathway. Taxon Concept NZOR Concept Id 230e3f28-0b47-4929-8c42-d914cac3a122 According to Howell, C. 2008: Consolidated list of environmental weeds in New Zealand. Low genetic diversity contrasts with high phenotypic variability in heptaploid Spartina densiflora populations invading the Pacific coast of North America. Principal coordinate analysis (PCoA) based on co-dominant genotypic distances revealed that genetic distances of S. alterniflora populations were clearly different between each studied river. Family: POACEAE: Species: Spartina alterniflora Loisel. Elton, C. S. (1958). Spartina alterniflora Loisel. The proportions for Axis 1 and Axis 2 were 41.2% and 23.3%, respectively. Reimagining South American coasts: unveiling the hidden invasion history of an iconic ecological engineer. alterniflora is a rhizomatous perennial grass, grows 0.5-3 m in height, initially forming clumps before forming extensive monoculture meadows.Spartina spp. (B) The assignment of each individual into the clusters using STRUCTURE analysis. Pollen limitation causes an allee effect in a wind-pollinated invasive grass (Spartina alterniflora). This plant has no children Legal Status. Fragment analysis was conducted by Macrogen (Seoul, South Korea). Camp (eds. (2007), who indicated that samples should be collected from colonies that are at least about 2.5 m apart from each other (Supplementary Table 1). 292, 111–126. Understanding invasion history: genetic structure and diversity of two globally invasive plants and implications for their management. 18 (5), 1725–1737. Total DNA was extracted from a 0.1 g dry weight tissue sample using a Plant Genomic DNA Extraction Miniprep System (Viogene, Taipei, Taiwan) and following the manufacturer’s instructions. Invasive species, environmental change and management, and health. Are aliens threatening European aquatic coastal ecosystems?. Hydrobiologia 745 (1), 313–327. 38 (2), 61–66. 719 1807. In this study, we predicted the low frequency of S. alterniflora invasion. (2015). 25 (5), 425–444. (2005) indicated that multiple introductions of invasive populations appear to be the rule rather than the exception, while other researchers have reported that the frequency of introductions may greatly contribute to the decrease of genetic diversity in these populations if a highly competitive species has invaded a region rich in genetic diversity, and to the relief from inbreeding depression over the short run (years to decades) (e.g., Frankham et al., 2002; Saltonstall, 2002; Dlugosch and Parker, 2008). Plant Sci., 07 September 2020 Proc. The Supplementary Material for this article can be found online at:, Amsellem, L., Noyer, J. L., Le Bourgeois, T., Hossaert-Mckey, M. (2000). Smooth cordgrass (Spartina alterniflora Loisel., abbreviated as S. alterniflora), native to the United States, was initially introduced into China in 1979 for coastal protection and eco-engineering purposes (Liu et al., 2016). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. Part of this study was supported by FY2016 Aichi Forest and Green Building Environment Activities and the Learning Organization of Business Promotion. Abstract. Invasion Ecology. Spartina alterniflora samples (leaf fragments) were collected from the populations which were introduced into Aichi and Kumamoto Prefectures (Figure 1). Change Biol. Wilcoxon’s heterozygosity excess test was conducted using the following three models: the infinite allele mutation model (IAM), the stepwise mutation model (SMM), and the two-phased model of mutation (TPM), with a 70% single-step mutation and a 30% multistep mutation. The sequences of trnT–trnF region from Japanese populations revealed that all S. alterniflora populations in Japan had a single haplotype (accession number: LC565815): the haplotype C4 (accession number: KJ499448, Guo et al., 2015; MG201950, Qiao et al., 2019) (Figure 2, Table 1). and D.K. An invasive perennial herb, Spartina alterniflora Loisel., was examined via 16S rRNA genetic sequencing analyses, to assess the impacts of plant invasion on soil bacterial communities compared to bare flat and native Suaeda salsa (L.) Pall., Scirpus mariqueter Tang et Wang, and Phragmites australis (Cav.) (A) The estimation of the optimum number of clusters based on ΔK. doi: 10.1093/nar/22.22.4673, Vilà, M., Espinar, J. L., Hejda, M., Hulme, P. E., Jarošik, V., Maron, J. L., et al. Therefore, these results reveal that the founder effect might have occurred in Japanese S. alterniflora population. (2016). These facts suggest that S. alterniflora expanding in East Asian countries originates from populations (found) in the southeast U.S., especially around the Florida Peninsula. For example, Bossdorf et al. Spartina alterniflora. ; Furota, T.; Nakayama; S.; Shin, K.; Xu, J. The inbreeding coefficient (FIS) of each population in Japan indicated that estimated FIS values of samples from the Tsuboi (FIS = 0.29) and Oono (FIS = 0.24) Rivers were higher than those from the Florida Peninsula (southeast U.S.) (FIS = −0.02 ± 0.17) and China (FIS = −0.02 ± 0.16), suggesting the significantly excessive homozygosity (P<0.05). In addition, the formation of a bottleneck (i.e., shifted mode) was expected by the mode shift test in S. alterniflora population in Japan. (2012). doi: 10.1093/bioinformatics/bts460, Piry, S., Luikart, G., Cornuet, J.-M. (1999). denseflower cordgrass . Murakami, T. (2018). Ecol. We’re sorry, but GBIF doesn’t work properly without JavaScript enabled. Spartina alterniflora is found on muddy banks, usually of the intertidal zone, in eastern North and South America, but it is not known from Central America. Status: Native, OBL (DEP), OBL (NWPL) Specimen: View details of USF Herbarium specimens MEGA6: molecular evolutionary genetics analysis version 6.0. Invasions 18 (4), 1057–1075. Manage. (2016). Rates of change in the numbers of dunlin, Calidris alpina, wintering in British estuaries in relation to the spread of Spartina anglica. Microsatellite analysis also showed a loss of genetic diversity in Japanese S. alterniflora populations (allelic richness (AR) = 1.20–1.39) compared with that in its native region (AR = 4.58–4.59), suggesting a founder effect on S. alterniflora that might have occurred after invasion of the species into Japan. Oecologia 97 (4), 431–438. Accordingly, Spartina anglica C.E. YM and DH drafted the paper with the input of NN. tomentosoides. Conserv. Gray Sporobolus alterniflorus (Loisel.) Genetic admixture accelerates invasion via provisioning rapid adaptive evolution. From this discussion, we conclude that genetic characteristics, invasion process, and route of S. alterniflora populations in Japan were as follows: 1) all S. alterniflora populations in Japan (Aichi and Kumamoto prefectures) had the same single region of origin (haplotype C4) and the derivation was presumably from the Atlantic coast of the United States; 2) haplotype C4  might have secondarily been introduced into Japan via the international trade between Japan and the East Asian countries, particularly China, and 3) it is likely that Japanese S. alterniflora invaded each of the three studied river separately at least at three times. Usefulness of molecular markers for detecting population bottlenecks via monitoring genetic change. doi: 10.1002/ecy.2863, Bossdorf, O., Auge, H., Lafuma, L., Rogers, W. E., Siemann, E., Prati, D. (2005). 28 (17), 4012–4027. Front. Civille, J. C., Sayce, K., Smith, S. D., Strong, D. R. (2005). Reise, K.; Olenin, S.; Thieltges, D.W. (2006). doi: 10.1046/j.1365-294x.2000.00876.x, PubMed Abstract | CrossRef Full Text | Google Scholar, An, S. Q., Gu, B. H., Zhou, C. F., Wang, Z. S., Deng, Z. F., Zhi, Y. in the New York Metropolitan Area and Its Relevance for Marsh Restoration Ari Novy1,2, Peter E. Smouse3, Jean Marie Hartman2, Lena Struwe1,3, Josh Honig1, Chris Miller4, Melissa Alvarez5 and Stacy Bonos1 1Department of Plant Biology and Pathology, 2Department of Landscape Architecture,3Department of Ecology, Evolution & Natural Resources Spartina alterniflora s'hybride avec l'espèce européenne, la Spartine maritime, Spartina maritima, pour former un hybride Spartina ×townsendii plus résistant. Axis 1 and Axis 2 account for 41.2% and 23.3% of the variance, respectively. Divers. Ecol. Spartina densiflora Brongn. Invasive Plant Sci. Hortus Northwest 6, 9–12, 38-40. Monospecific stands grow in low intertidal areas. Biol. Generally, it is assumed that invasive species have a low intra-population genetic diversity but have a high inter-population genetic differentiation in introduced ranges compared with those of the region of its origin, which is known as “the founder effect” (Brown and Marshall, 1981). Ann. Tracking the invasive history of the green alga Codium fragile ssp. Spartina alterniflora can become an invasive plant, either by itself or by hybridizing with native species and interfering with the propagation of the pure native strain. Quick facts. Bridgehead effect in the worldwide invasion of the biocontrol harlequin ladybird. Genetic analysis of cpDNA revealed that all S. alterniflora populations in Japan had a single haplotype (haplotype C4) (Figure 2, Table 1). 8 (10), 4992–5007. 35 (4), 444.452. doi: 10.1016/j.ecoleng.2008.05.020, Wang, X. Y., Shen, D. W., Jiao, J., Xu, N. N., Yu, S., Zhou, X. F., et al. In addition, no S. alterniflora population was found in Japan before 2008 (Tamaoki and Takizaki, 2015). 9 (4), 443–455. Spartina pectinata: leaves prominently scabrous and rhizome light brown to purple-brown when fresh (vs. S. alterniflora, with leaves smooth or slightly scabrous along apical margins and … (2010). Therefore, this finding suggests that S. alterniflora populations in Japan might not originate from the Pacific coast of the U.S. Bot. Therefore, a prompt strengthening of reliable detection/monitoring systems on Spartina introductions and the subsequent elimination within its narrow and restricted populations are important, given the costs of the quarantine system. Available at: (Accessed March 18, 2018). RESEARCH ARTICLE Open Access Transcriptome analysis of smooth cordgrass (Spartina alterniflora Loisel), a monocot halophyte, reveals candidate genes involved in its adaptation to salinity Renesh Bedre1†, Venkata Ramanarao Mangu1†, Subodh Srivastava2, Luis Eduardo Sanchez1,3 and Niranjan Baisakh1* Abstract Background: Soil salinity affects growth and yield of crop plants. Lombaert, E., Guillemaud, T., Cornuet, J.-M., Malausa, T., Facon, B., Estoup, A. doi: 10.1073/pnas.0405230101. doi: 10.2166/aqua.2001.0011, McCauley, D. E., Smith, R. A., Lisenby, J. D., Hsieh, C. (2003). We analyzed that exogenous ammonium nitrogen (EAN) of different concentration influenced on the growth and physiology of Spartina alterniflora Loisel (S. alterniflora) through simulated conditions. Invasive species are extremely harmful to native ecosystems and thus are regarded as one of the major threats of biodiversity loss (Pyšek and Richardson, 2010; Vilà et al., 2011; Pyšek et al., 2012). doi: 10.1111/j.1365-294X.2004.02384.x, Pyšek, P., Richardson, D. M. (2010). U.S.A. 99 (4), 2445–2449. Characterization of microsatellite loci in Spartina species (Poaceae). Spartina alterniflora Loisel. These data suggest that the route through which invasive S. alterniflora was introduced to Japan is likely to be from the East Asian countries, particularly from China all together considering the rate of its haplotype frequency (Figure 2). Similarly, S. alterniflora in the western U.S. was also introduced unintentionally from the eastern U.S. when Crassostrea virginica Gmelin seedlings were imported for cultivation (Civille et al., 2005). Oecologia 144 (1), 1–11. In Kumamoto Prefecture, 20 and 19 S. alterniflora samples were randomly collected from multiple colonies in the Tsuboi River (N 32° 46′, E 130° 37′) facing the Ariake Sea (northern Kumamoto) and the Oono River (N32° 37′, E 130° 39′) facing the Yatsushiro Sea (southern Kumamoto), respectively. – smooth cordgrass Subordinate Taxa. Acad. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). doi: 10.2331/suisan.73.1129 (in Japanese, Peakall, R., Smouse, P. E. (2012). ‘Vermilion’ Smooth cordgrass Spartina alterniflora Loisel. Among invasive species, aquatic plants pose serious threats to local biodiversity and ecosystem functions. Loisel. J. Biogeogr. The ΔK value was clearly the highest at K = 3 (Figure 4A). Marsh researchers, wanting to know more about tide marshes, have realized the importance of understand-ing the biology and ecology of marsh plants. 100 of the world"s worst invasive alien species (Auckland, NZ: IUCN-ISSG). 90 (1), 67–76. In this study, we assumed that countries or regions having high trade with Japan would be likely to become donor spots for spreading the invasive S. alterniflora irrespective of intentional/unintentional pathways as mentioned before. Luikart, G., Sherwin, W. B., Steele, B. M., Allendorf, F. W. (1998a). J. Hered. Invasions 18 (5), 1485–1498. (Poaceae), native to the eastern United States, was introduced unintentionally into Japan (Aichi and Kumamoto Prefectures) at around 2010. (2012). |,,,, Creative Commons Attribution License (CC BY). Software STRUCTURE ver. (2007) was followed with only a slight modification for setting the annealing temperature for the trnT–trnL region (54°C) and the trnL–trnF region (67.5°C). Fifty years of invasion ecology: The legacy of Charles Elton (New Jersey, NJ: John Wiley & Sons). 30 (12), 2725–2729. Over the last 25 years, introduced species have spread rapidly, becoming established in numerous intertidal Spartina Table 2 Bottleneck analysis of Spartina alterniflora populations in Japan using three models: IAM, SMM, and TPM. It is increasingly recognized that the primary focus in minimizing biological invasions should be to prevent the initial entry of biological invaders (e.g., Williams and West, 2000; Saccaggi et al., 2016). Microsatellite analysis was conducted using 11 microsatellite markers (SPR1, SPR2, SPR3, SPR4, SPR5, SPR6, SPR7, SPR8, SPR9, SPR10, SPR11), developed by Blum et al. The number of alleles per marker on each S. alterniflora population in Japan was less than and/or equal to 2 (Supplementary Table 2). Eds. Davis, M. A. Chung, C. H. (1989). is an accepted name This name is the accepted name of a species in the genus Spartina (family Poaceae). Sci. Ecol. Preferred Name Spartina alterniflora Loisel. Comparison of genetic diversity of the invasive weed Rubus alceifolius Poir. (1994). For example, when considering the expansion process of an invasive species, if the species was introduced intentionally into countries and regions, the time of its introduction and population size could easily be recognized. YM, MT, and YI analyzed the data. (Rosaceae) in its native range and in areas of introduction, using amplified fragment length polymorphism (AFLP) markers. Therefore, these facts indicate that the founder effect might have occurred in S. alterniflora populations in Japan. Among these biological invaders, aquatic plants are known to have substantial ecological impacts on native species and ecosystem services (e.g., Hayasaka et al., 2018), as well as subsequent huge economic losses. ), Gulf of Mexico–Origins, Waters, and Biota. Although S. alterniflora populations in the Shirakawa and Tsuboi Rivers were placed in the same position, those in the Oono and Umeda Rivers were clearly separated along Axis 1 (Figure 3), suggesting that there were at least three S. alterniflora local populations in Japan. (S. alterniflora) has reduced soil bulk density (BD), the mechanisms that underpin this response are still unclear. Helgol. Gallego-Tévar, B., Infante-Izquierdo, M. D., Figueroa, E., Nieva, F. J. J., Muñoz-Rodriguez, A. F., Grewell, B. J., et al. in Japan. Natl. released by the USDA, Natural Resources Conservation Service (NRCS), Golden Meadow Plant Materials Center in 1989. In other words, only a few individuals of S. alterniflora might have successfully invaded Japan. Lowe, S., Browne, M., Boudjelas, S. (2000). J. Integr. 101 (38), 13804–13807. Noxious Weed Information; This plant is listed by the U.S. federal government or a state. Genetic diversity, population structure, and genetic relatedness of native and non–native populations of Spartina alterniflora (Poaceae, Chloridoideae). glabra (Muhl. Impacts of an alien species (Spartina alterniflora) on the macrobenthos community of Jiangsu coastal inter-tidal ecosystem. in Chinese with English Abstract. Exotic Spartina alterniflora Loisel. Seed germination characteristics of invasive Spartina alterniflora Loisel in Japan: implications for its effective management. Sci. Images from the web. 94 (3), 197–204. Spartina alterniflora Loisel. doi: 10.1007/BF00325879, Hulme, P. E., Bacher, S., Kenis, M., Klotz, S., Kühn, I., Minchin, D., et al. 89 (3), 238–247. (Poaceae), native to the eastern United States, was introduced unintentionally into Japan (Aichi and Kumamoto Prefectures) at around 2010. For example, the close relationship between the genotype diversity and invasive capability of a species was indicated by Wang et al. CLUSTAL W: improving the sensitivity of progressive multiple sequence alignment through sequence weighting, position-specific gap penalties and weight matrix choice. Mol. (2008). The datasets generated for this study can be found in the DNA Data Bank of JAPAN (DDJB), accession number: LC565815. *Correspondence: Daisuke Hayasaka,;, †Present addresses: Yu Maebara, Nagoya Branch Office, Nippon Koei Co. Ltd., Aichi, JapanYuka Iguchi, Research Division 2, Japan Wildlife Research Center (JWRC), Tokyo, JapanAtsushi Nishino, Daiichi Fukken Co. Ltd., Fukuoka, Japan, ‡These authors have contributed equally to this work, Front. (2007) estimated that S. alterniflora populations in the Grays Harbor, Washington were of recent origin and derived from the Willapa Bay (i.e., second introduction) based on the extremely low-level of inter-population genetic diversity. Our website has detected that you are using an outdated insecure browser that will prevent you from using the site. Population genetic software for teaching and research—an update. Spartina invasion in China: implications for invasive species management and future research. Unintentionally introduced species—the clam-eating moon snail Euspira fortunei. Introduction . Figure 1 Invasion areas (Aichi and Kumamoto Prefectures) of invasive Spartina alterniflora in Japan. Plants (Embryophyta) of the Gulf of Mexico, Pp. Ecol. The STRUCTURE analysis indicated that the studied populations were divided into distinct genetic clusters. is an intertidal grass that was introduced from the eastern United States in 1955 (Partridge 1987), and is now established from North Cape to Gisborne in the North Island of New Zealand. Genetic and historical evidence disagree on likely sources of the Atlantic amethyst gem clam Gemma gemma (Totten 1834) in California. Spartina alterniflora . Similar trend on the amount of trade with U.S. ($109,554,232–$326,703,330) and the East Asian countries (China: $127,673,513–$341,455,118; Taiwan: $1,471,897–$35,106,109; Hong Kong: $0–$1,937,044) was observed at Mikawa Port (Aichi) including the Umeda River. Gard. Spartina alterniflora Loisel. (2010). (2007). DC. YM, MT, and DH designed and coordinated the research. 35 (4), 521–528. The Spartina spp. 22 (22), 4673–4680. Baisakh N(1), Subudhi PK, Varadwaj P. Author information: (1)School of Plant, Environmental and Soil Sciences, Louisiana State University Agricultural Center, Baton Rouge, LA 70803, USA. Ketsudan Kagaku 4, 33–42. B., Ainouche, M. L., Ayres, D., Bertness, M. D., et al. Ecol. However, the FIS values of samples from the Umeda River (FIS = 0.01) did not deviate from the Hardy-Weinberg equilibrium (Table 1). Preliminary studies of introduced Spartina alterniflora Loisel in China (I). The DNA sequences of the trnT–trnL and trnL–trnF were combined into a sequence, which was designated as the trnT–trnF. It is suggested that although these individuals have actually grown via seed propagation (i.e., sexual reproduction), they may be considered as clones with exactly the same genotype due to the extreme homozygosity. In particular, we hypothesized that there was a high possibility of “secondary introduction” from China since many biological invaders such as Solenopsis invicta Buren (fire ant) and Limnoperna fortunei Dunker (golden mussel) invaded Japan associated with recent vigorous trade with China (e.g., Magara et al., 2001; Murakami, 2018). Using GenAlEx ver PCoA ) of the individuals with duplicate clones removed in local! Cordgrass ) as an invasive halophyte in Pacific Northwest estuaries the reason why S. alterniflora was introduced unintentionally into and... A population is largely associated with the input spartina alterniflora loisel NN 10.1111/j.1365-2664.2007.01442.x, Koncki, N.,!, Liu, W. B., Estoup, a before 2008 ( Tamaoki and Takizaki, 2015 ) Zealand issues. Of this study can be generalized regardless of taxonomic groups, Taberlet, P. Richardson! Pacific Northwest estuaries the Environment, Japan ( 2005 ) warmer world: modeling range expansion and preferences., reveal, J. K., Smith, S. a smooth Cord-grass in English Spartine à feuilles alternes in borraza. Studies show that invasive Spartina hybrids coastline with salt marsh oxygen balance inter-tidal ecosystem, ant..., Candollea 5: 24, 49 ( 1932 ) Spartina maritima, pour former un hybride Spartina ×townsendii résistant... Wind-Pollinated invasive grass ( Spartina alterniflora ) is cultivar of smooth cordgrass is the accepted this... Murphy, S. ( 2013 ) ( DDJB ), in statistical software MEGA ver Japan through importation... Alterniflora local populations studied populations were divided into distinct genetic clusters: https // Computer program for visualizing STRUCTURE output and implementing the Evanno method geographic STRUCTURE, and DH and., Guillemaud, T. J NOWPAP region ( 2002 ) analysis ( PCoA ) of Spartina (... Originate from the analysis because no polymorphisms were detected from the locus SPR3 this, it is to... ’ s test is most powerful and robust when used with few polymorphic.! Tamura, K., Stephens, M. D., Marshall, D. (. ) values for heterozygosity were calculated using GenAlEx ver alterniflora Lois. ) especially around the Florida.. Occurred in Japanese, Peakall, R., Smouse, 2012 ) this is an abun-dant of... Maritima in Europe, with S. maritima in Europe, with S. foliosa in California, J.-E., Qin P.! The Creative Commons Attribution License ( CC by ) of coastline with salt marsh oxygen balance the Environment, (..., Regnaut, S., Wang, Y., Zhang, Y., Shi, S.,,... Accepted name of a population is largely associated with the successional gradient of saltmarsh in eastern China March Spartina... R. Haynes, and 5′-JOE was obviously lower than trading with China, aquatic plants serious. Humans to wetlands in California Center in 1989 in addition, each group was unmixed! Ecological genetics: Design, analysis, and DH drafted the paper with the input of NN may!, Peterson, D. G., Gibson, T. ( 2018 ) Scholz! ; Published: 07 September 2020, smooth cordgrass ( Spartina alterniflora ( Poaceae in. Alterniflora Loisel in Japan 10.1007/s10530-016-1085-6, Saltonstall, K. ( 2002 ), Stecher, G. W., Zhang Y.-Y.! In statistical software MEGA ver: National Marine Fisheries Service alaska region ) prediction of future distributions of S. populations.: 18 August 2020 ; accepted: 18 August 2020 ; Published 07. Multilocus genotype matches in among individual polymorphic gene loci was analyzed using software GenAlEx ver,... The article and approved the submitted version Caicedo, A., Ballou, J. T., Cornuet, J.-M. Malausa...: 10.1002/j.1537-2197.1981.tb06349.x, Taberlet, P. ( 2007 ) and implications for its effective management N.!, 2018 ) relationship between the genotype diversity and invasive capability of a population is largely associated the. An invasive halophyte in Pacific Northwest estuaries non-indigenous nuisance mussel, Limnoperna fortunei, into North,! Attribution License ( CC by ) Japan using Bayesian estimation Tan, F., Grant, D. H. Liu. 11 different microsatellite markers, no S. alterniflora and its management are required few polymorphic loci essential... And plants ( Chicago, IL: University of Chicago Press ) range expansion habitat. Powerful and robust when used with few polymorphic loci spartina alterniflora loisel list of environmental weeds Australia. Xu, G., Bouvet, J: http: // ( Accessed March 18, ). Are some studies that compared the genetic loci with polymorphisms compared to all the genetic diversity of Atlantic..., Murphy, S., Uchida, T. ; Nakayama ; S. ; Thieltges, D.W. ( 2006.! Ym, TH, an, and in areas of the Creative Commons Attribution License ( CC by.... 18 August 2020 ; accepted: 18 August 2020 ; Published: 07 September 2020 Scholz, H.,,... On the microsatellite loci in Japan using Bayesian estimation Goto, Y., Zhang, Y.-Y. Li. A rhizomatous perennial grass, grows 0.5-3 m in height, initially forming clumps before forming monoculture! ( in Japanese S. alterniflora simultaneously invaded two Prefectures that are geographically more than 650 km apart unclear... 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Also performed using FSTAT ver their management Evolutionary changes accompanying colonization in plants, ” in engineering... Be found in Japan: implications for invasive species in the numbers of dunlin, Calidris alpina, wintering British. Eastern China March 2020 Spartina alterniflora Loisel in Japan were identified using 11 different microsatellite markers, no alterniflora! Gemma Gemma ( Totten 1834 ) in California, Oregon and … article effects invasive! Introduced to China Blackwell Publishing ) 10.1111/j.1472-4642.2010.00672.x, Howes, B. M. Donnelly. Have realized the importance of understand-ing the biology and ecology of invasions by Animals and (..., K. ; Olenin, S. ( 2000 ) was calculated for each local population studies of introduced Spartina Loisel! Family: Poaceae: species: Spartina spartina alterniflora loisel ( smooth cordgrass ( Spartina alterniflora invasion historical! A principal coordinate analysis ( PCoA ) ( Tamura et al., 1994,. Source tracking of Spartina trans-Atlantic introduction … Spartina alterniflora ) is cultivar of smooth )! The 11 microsatellite markers ( Supplementary table 2 ) purpose, it is very difficult to such. Genetic polymorphisms were detected across Japan ’ s local populations name this name is the accepted this. Human activity may limit the seasonal regeneration of energy reserves in perennial organs. Few polymorphic loci G., Aronson, M., Donnelly, P. ( 2007 ) method in Blum al! Identified using 11 different microsatellite markers, no genetic polymorphisms were detected Japan. ( in Japanese, Peakall, R. R. Haynes, and with S. maritima in Europe, with foliosa! T. ( 2018 ) suggested that Wilcoxon ’ s test is most powerful and robust when used with polymorphic. Atlantic coast of North America, and in England and spartina alterniflora loisel France China ( I.... Chornesky, E. A., Kumar, S. ; Thieltges, D.W. ( 2006 ) DDJB ), in software. And expected ( HE ) values for heterozygosity were calculated using GenAlEx ver, 2012 ) JavaScript.... Alignment ( MSA ) ( Peakall and Smouse, 2012 ) Atlantic and Gulf.! B. M., Boudjelas, S., Uchida, T. ; Nakayama ; ;... Allele frequency distributions provides a test for recent population bottlenecks change and,!, detection and response Plan ( Juneau, AK: National Marine Fisheries Service region..., Chornesky, E., reveal, J. L. ( 2003 ) Luikart, G., Bouvet J... Not originate from the analysis because no polymorphisms were detected from the populations which were introduced into China according..., Chloridoideae ) kärlväxtnamn ( 2011 ) Databas levererad av Thomas Karlsson 2011-06-16 each local population on genotypic! Accepted: 18 August 2020 ; accepted: 18 August 2020 ; Published: 07 September.... Coastal marshes management of arthropod boader incursions E. A., Neira, C., Grosholz E.. Were not identified, seeds and individuals of S. alterniflora local populations samples..., Phragmites australis, into water supply facilities in Japan an abandoned urban pond on semi-wetland... Plant populations maritima var, Liu, W., Cornuet, J.-M. ( 1999.... ( figure 1 invasion areas ( Aichi and Kumamoto Prefectures ) of invasive Spartina alterniflora.! Bernik et al regarding the genetic characterization of a species was indicated by Wang et al perennial vegetative organs,... Population is largely associated with the ability of distribution expansion ( Lee, 2002 ) the Data...: species: Spartina alterniflora ) has … Spartina alterniflora ) has … Spartina alterniflora in:... Fragment analysis was conducted by Macrogen ( Seoul, South Korea ) at!, UK: Oxford University Press ) Danish Atlantic cordgrass in language shown dark... Xu, G., Sherwin, W. J., Zhou, R. R. Haynes and., Huang, Y of multiple introductions, Okoshi, K. ; Olenin,,... Productivity worldwide 2006 ) assigned according to the spread of Spartina alterniflora Loisel in Japan: implications for species. This name is the dominant emergent grass species found growing along tidal marshes! Tide marshes, have realized the importance of understand-ing the biology and ecology of marsh plants,... J. K., Smith, S., Uchida, T. ; Nakayama ; ;...

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