spartina alterniflora loisel

(1991). In Japan, Spartina alterniflora Loisel (smooth cordgrass), a plant native to the Atlantic coast of North America and the Gulf of Mexico, was first detected in 2008 in Aichi Prefecture and in 2009 in Kumamoto Prefecture, followed by identification in multiple rivers and tidal flats in both prefectures (i.e., unintentional introduction) (Tamaoki and Takizaki, 2015). Mol. Res. 8 (4), 436–450. doi: 10.1046/j.1365-294X.2003.01992.x. Genetic and historical evidence disagree on likely sources of the Atlantic amethyst gem clam Gemma gemma (Totten 1834) in California. Despite this, it took approximately 6 years from its first detection to the start at the eradication project. (Poaceae) Introduced Unintentionally Into Japan and Its Invasion Pathway. Here, the genetic structure of invasive S. alterniflora in Japan and its origin were assessed by analyzing the degree of genetic diversity and genetic mixing in Japanese populations, using chloroplast and nuclear molecular markers. Scudder, G. G. E., Reveal, J. L. (Pittsburgh, PA: Carnegie–Mellon University), 351–363. excluded, secreted or accumulated the major seawater ions (Cl-, SO 2-4, Na +, K +, Mg 2+, and Ca 2+) was investigated under varying salinity treatments.From a quantitative viewpoint, ion exclusion was most prominent and accounted for 91–97% of the theoretical maximum ion uptake as a result of transpiration and growth. (2009). Family: POACEAE: Species: Spartina alterniflora Loisel. doi: 10.1007/BF00037152. A TaKaRa PCR Thermal Cycler (TaKaRa BIO, Shiga, Japan) was used for the PCR assay. doi: 10.1093/jhered/90.4.502, Prentis, P. J., Sigg, D. P., Raghu, S., Dhileepan, K., Pavasovic, A., Lowe, A. J. marshhay cordgrass . Thus, prediction of future distributions of S. alterniflora and its management are required. J. Jap. tomentosoides. doi: 10.1111/mec.15192. Taxon Concept NZOR Concept Id 230e3f28-0b47-4929-8c42-d914cac3a122 According to Howell, C. 2008: Consolidated list of environmental weeds in New Zealand. 12 (12), 3227–3235. After 1979, seeds and individuals of S. alterniflora were intentionally introduced into China from multiple areas of the Atlantic coast of the U.S. Ecology 87 (2), 419–432. The authors also wish to thank Moe Nakagawa, Ryu Ikeda, Kota Kohara and Yoshinori Taruma (Kindai University) for helping with S. alterniflora sampling. doi: 10.1046/j.1442-9993.2000.01081.x. Since the cause of a lower genetic diversity among invasive Spartina species is of great interest, we discuss below the reason why S. alterniflora populations had lower genetic diversity when invading Japan. (2001). 89 (3), 238–247. Supplements to the Grassess (Poaceae) in Taiwan (II). Genetic variation of Spartina alterniflora intentionally introduced to China. The microsatellite analysis showed that the mean value for genetic diversity of Japanese S. alterniflora samples were as follows; the Umeda River (h = 0.34, AR = 1.34 ± 0.22), Tsuboi River (h = 0.24, AR = 1.24 ± 0.24), and Oono River (h = 0.39, AR = 1.39 ± 0.20). Ecological Genetics: Design, Analysis, and Application (Malden, MA: Blackwell Publishing). 25 (1), 95–109. Tamura, K., Stecher, G., Peterson, D., Filipski, A., Kumar, S. (2013). Spartina alterniflora Loisel. doi: 10.1016/j.ecoleng.2008.06.007, Keywords: biological invasion, chloroplast DNA, founder effect, genetic structure, microsatellite, secondary introduction, smooth cordgrass, trade history, Citation: Maebara Y, Tamaoki M, Iguchi Y, Nakahama N, Hanai T, Nishino A and Hayasaka D (2020) Genetic Diversity of Invasive Spartina alterniflora Loisel. Gray Sporobolus alterniflorus (Loisel.) PCR products were purified using NucleoSpin Extract II (Macherey–Nagel, Düren, Germany) and then were used as a template for the cycle sequencing reaction. Coastal eutrophication has become a driver of coastal wetlands loss. Monospecific stands grow in low intertidal areas. (2015). Genetic diversity, population structure, and genetic relatedness of native and non–native populations of Spartina alterniflora (Poaceae, Chloridoideae). Alternate Names . 719 1807. Natl. Our website has detected that you are using an outdated insecure browser that will prevent you from using the site. Genetic Variation of Spartina alterniflora Loisel. Mol. Vegetative regeneration of natural Spartina alterniflora Loisel. (2005). doi: 10.1007/s10530-016-1096-3, Blum, M. J., Sloop, C. M., Ayres, D. R., Strong, D. R. (2004). 15 (5), 822–830. Notes 4 (1), 39–42. on Soil Organic Carbon Fractions and Stock Jianxiang Feng 1, Shugong Wang 2,3,*, Shujuan Wang 2,3, Rui Ying 1, Fangmin Yin 1, Li Jiang 1 and Zufu Li 1 1 School of Life Sciences, Sun Yat-sen University, Guangzhou 510275, China; fengjx23@mail.sysu.edu.cn … A global assessment of invasive plant impacts on resident species, communities and ecosystems: the interaction of impact measures, invading species’ traits and environment. The Spartina spp. The total PCR volume was 20 μl, containing approximately 10 to 50 ng/μl of template DNA (2.0 μl), 10× NH4 reaction Buffer (2.0 μl), 10 mM dNTP mix (1.6 μl), 50 mM MgCl2 (1.6 μl), 0.2 μl of each 100 pM primer pair, and 5 U/µl of Biotaq™ DNA polymerase (0.1 μl) (Nippon Genetics, Tokyo, Japan) were used. is an abun-dant inhabitant of North American Atlantic coastal marshes. doi: 10.1046/j.1365-294x.1998.00414.x, Luikart, G., Allendorf, F. W., Cornuet, J.-M., Sherwin, W. B. J. Hered. Groups A, B, and D consisting of a single haplotype are shown in dark grey, black and light grey, respectively. Soc Water Environ. Alaska Spartina Prevention, Detection and Response Plan (Juneau, AK: National Marine Fisheries Service Alaska Region). Plants growing under good conditions reach 8 feet (2.5 m) tall, while those growing in the high salt marshes, especially at edges of salt pans, may be only 16 inches (40 cm) tall, including … Lockwood, J. L., Hoopes, M. F., Marchetti, M. P. (2007). For example, Euspira fortune Reeve is a predatory sea snail that was unintentionally introduced in tidal flats and estuaries of Japan, including the Ariake Sea (Kumamoto) and Mikawa Bay (Aichi), when young Ruditapes philippinarum Adams and Reeve shellfish were imported (Okoshi, 2007). Grass family (Poaceae) Download PDF version formatted for print (311 KB) **NOTE: Smooth cordgrass is native to coastal states of eastern and southern U.S. Environ. doi: 10.1111/j.1365-2699.2007.01764.x, Bortolus, A., Carlton, J. T., Schwindt, E. (2015). This invasive species could easily and rapidly spread to estuarine areas of Japan via vigorous trade and transport, making the prediction of its future invasion necessary. 2009. The Ecology of Invasions by Animals and Plants (Chicago, IL: University of Chicago Press). denseflower cordgrass . In addition, serious ecological impacts of Spartina species on native aquatic ecosystems through competitive exclusion (Goss-Custard and Moser, 1988; Wan et al., 2009; Zhou et al., 2009; Morgan and Systma, 2010) and changes in community and trophic structures (Simenstad and Thom, 1995; Levin et al., 2006; Bortolus et al., 2015) were found due to their expansion. ... Daehler, C. C.; Strong, D. R. Variable Reproductive Output Among Clones of Spartina alterniflora (Poaceae) Invading San Francisco Bay, California: The Influence of Herbivory, Pollination, and Establishment Site // American Journal of Botany. Software STRUCTURE ver. Synonyms: Bridgehead effect in the worldwide invasion of the biocontrol harlequin ladybird. 6.5 (Peakall and Smouse, 2012). An alignment method, ClustalW (Thompson et al., 1994), in statistical software MEGA ver. Glucose was not detected in the leachate of either growth form. Bioinformatics 28 (19), 2537–2539. (2012). 34 (12), 2055–2069. doi: 10.1073/pnas.0405230101. Dlugosch, K. M., Parker, I. M. (2008). 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). Richardson, D. M. (2011). doi: 10.3354/meps292111, Okoshi, K. (2007). Conserv. Phenotypic and genetic differentiation between native and introduced plant populations. common cordgrass . Mol. Divers. ★ indicates the region estimated as the place that S. alterniflora was initially introduced into China, according to Bernik et al. Xu, G. W., Zhou, R. Z. 47 (3), 183–191. Spartina alterniflora, a native species at the east coast of North America, is currently the focus of increasing management concern due to its rapid expansion in coastal China.To better understand the plant traits associated with the success of invasion, we examined the genetic variation and the possible existence and distribution of ecotype hybrids and ecotype mixtures of the species in China. Methods and approaches for the management of arthropod boader incursions. Spartina alterniflora Loisel. Conserv. Divers. ex Elliott) St.-Yves, Candollea 5: 48 (1932) Spartina maritima var. Therefore, it is important to strengthen the quarantine control on the importation of commodities, especially of transport vehicles at potential donor spots (i.e., border control/border biosecurity system), and to share information networks on invasive species between each region/port for minimizing further risks of biological species such as Spartina. On the other hand, low g values were found in samples from the Shirakawa River (g = 0.33) and Guangdong province in China (g = 0.32), where almost all analyzed samples had the same genotype. alterniflora (Loisel.) Invasions 18 (4), 1057–1075. 292, 111–126. The genotypes of S. alterniflora populations in Japan were identified using 11 different microsatellite markers (Supplementary Table 2). Biol. YM, MT, and DH designed and coordinated the research. Introduction . 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). YM, MT, and YI analyzed the data. Brown, A. H. D., Marshall, D. R. (1981). 100 of the world"s worst invasive alien species (Auckland, NZ: IUCN-ISSG). Therefore, these results reveal that the founder effect might have occurred in Japanese S. alterniflora population. doi: 10.1614/IPSM-D-15-00020.1, Lee, C. E. (2002). Fragment analysis was conducted by Macrogen (Seoul, South Korea). Ecol. Nucleic Acids Res. 18 (5), 1725–1737. 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). Ecological impacts of invasive alien plants: a meta-analysis of their effects on species, communities and ecosystems. Invasion significantly shifts soil bacterial communities with the successional gradient of saltmarsh in eastern China March 2020 The DNA sequences of the trnT–trnL and trnL–trnF were combined into a sequence, which was designated as the trnT–trnF. doi: 10.1007/s10531-005-2575-5, Zhou, H.-X., Liu, J.-E., Qin, P. (2009). Biodiversity. Saltmarsh cordgrass, oystergrass, and saltwater cordgrass . 261–284 in Felder, D.L. Discussion. 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. The principal coordinate analysis and The STRUCTURE analysis indicated that no gene mixing among Japanese local populations (Aichi, northern and southern Kumamoto) was observed, indicating that Spartina invasion occurred independently into these regions. Spartina alterniflora Loisel. Luikart, G., Sherwin, W. B., Steele, B. M., Allendorf, F. W. (1998a). Spartina alterniflora Loisel. doi: 10.1111/j.1472-4642.2010.00672.x, Howes, B. L., Teal, J. M. (1994). Rev. 28 (17), 4012–4027. Guo, W., Qiao, S., Wang, Y., Shi, S., Tan, F., Huang, Y. 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. in Chinese with English Abstract. Mol. Plant Symbol = SPAL. in the mangrove ecosystems of China was reduced using Sonneratia apetala Buch.-Ham. 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. Spartina invasion in China: implications for invasive species management and future research. De plus, Spartina ×townsendii a produit par doublement chromosomique une nouvelle forme nommée Spartina anglica dont la vitalité met en péril la biodiversité des sites qu'elle colonise [ 1 ] . J. Bot. Spartina alterniflora. For example, the most likely invasion pathways of S. alterniflora in Willapa Bay, Washington, on the Pacific coast of the U.S. was the transport and translocation of oysters for cultivation via interstate railroad after the 1890s (Civille et al., 2005). 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. The extent to which Spartina alterniflora Loisel. Evolutionary genetics of invasive species. Plant Mol. Impact Factor 4.402 | CiteScore 7.8More on impact ›, National Tropical Botanical Garden, United States, Faculty of Science, University of South Bohemia, Czechia. (Poaceae), native to the eastern United States, was introduced unintentionally into Japan (Aichi and Kumamoto Prefectures) at around 2010. doi: 10.1073/pnas.032477999, Schaal, B. Invasion risk in a warmer world: modeling range expansion and habitat preferences of three nonnative aquatic invasive plants. Therefore, it is important to strengthen the quarantine control on the importation of commodities, especially of transport vehicles at potential donor spots (i.e., border control/border biosecurity system), to decrease further risks of various biological invaders (Chornesky and Randall, 2003; Xu et al., 2006) including that of Spartina species (Castillo et al., 2018; Gallego-Tévar et al., 2019). Here, the distribution and structure of the genetic variation of S. alterniflora in Japan were examined using chloroplast DNA (cpDNA) and microsatellite genotyping analyses for clarifying its invasion route and process. Biol. PloS One 5 (3), e9743. Populations of S. alterniflora in the Grays Harbor, Washington (haplotype B) and Taiwan (haplotype C4), which had only a single haplotype as well as Japan (Figure 2), were unintentionally and secondarily introduced from the Willapa Bay, Washington (the Pacific coast of the U.S.) (Civille et al., 2005) and the vicinity of Fujian (China) (Lin et al., 2015), respectively. Understanding invasion history: genetic structure and diversity of two globally invasive plants and implications for their management. doi: 10.1002/j.1537-2197.1981.tb06349.x, Taberlet, P., Gielly, L., Pautou, G., Bouvet, J. doi: 10.1002/ecy.2863, Bossdorf, O., Auge, H., Lafuma, L., Rogers, W. E., Siemann, E., Prati, D. (2005). Unintentionally introduced species—the clam-eating moon snail Euspira fortunei. 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: 10.1007/s10750-014-2117-9, Hayasaka, D., Fujiwara, S., Uchida, T. (2018). Therefore, the most likely invasion route may have been the arrival through a transport vehicle (i.e., stowaway) (Hulme et al., 2008). The significant excessive homozygosity on Japanese S. alterniflora populations was observed in the infinite allele mutation model (IAM), the stepwise mutation model (SMM), and the two-phased model of mutation (TPM) (P<0.05). Geographic structure, genetic diversity and source tracking of Spartina alterniflora. doi: 10.1111/j.1365-3180.2007.00559.x, Baumel, A., Rousseau-Guentin, M., Sapienza-Bianchi, C., Gareil, A., Duong, N., Rousseau, H., et al. (e.g., North Carolina, Georgia, and Florida) for eco-engineering purposes (i.e., reclamation of tideland) (Xu and Zhou, 1985; Wan et al., 2009). (2007). U.S.A. 99 (4), 2445–2449. Am. Spartina anglica C.E. All names of the haplotypes obtained in this study were assigned according to the method of Blum et al. doi: 10.1093/jhered/esg060, Scholz, H., Chen, C.-W., Jung, M.-J. Ecol. 17 (8), 1881–1887. Results of the microsatellite analysis made it clear that some S. alterniflora individuals (St. 13, 15, 16, and 18) in the Tsuboi River (northern Kumamoto) had a heterozygous at only one locus, while two individuals growing sympatrically (St. 14 and 17) had a homozygous at all of the loci (Supplementary Table 2). Ecol. Goudet, J. J. Appl. From these facts, we cannot deny the possibility that S. alterniflora was introduced unintentionally into Japan through the importation of cultured shellfishes. Two additional monosaccharides were found but were not identified. 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. Tracking the invasive history of the green alga Codium fragile ssp. J. Gall. The record derives from WCSP (data supplied on 2012-03-23) which reports it as an accepted name (record 443751) with original publication details: Fl. The ΔK value was clearly the highest at K = 3 (Figure 4A). (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). Are aliens threatening European aquatic coastal ecosystems?. doi: 10.1111/j.1365-2664.2007.01442.x, Koncki, N. G., Aronson, M. F. J. (2019). 38 (2), 61–66. Table 1 Information on the genetic diversity of invasive Spartina alterniflora based on the microsatellite loci in Japan. Mo. released by the USDA, Natural Resources Conservation Service (NRCS), Golden Meadow Plant Materials Center in 1989. In addition, the genetic characterization of a population is largely associated with the ability of distribution expansion (Lee, 2002). Thus, to validate this hypothesis, trade histories were compared between countries/regions where S. alterniflora has grown (the United States, China, Taiwan, Hong Kong) (Blum et al., 2007; Guo et al., 2015; Bernik et al., 2016) and the ports nearest to each studied river in Japan (i.e., Kumamoto Port, Yatsushiro Port, and Mikawa Port) using historical trade data from the 2003 to 2013 in the Global Trade Atlas (https://www.gtis.com/gta/). Evol. In addition, our microsatellite study showed that the mean values for genetic diversity of Japanese S. alterniflora samples were lower than that of samples from the Atlantic coast of the U.S. (h = 0.42 ± 0.08, AR = 4.59 ± 1.24) and the Florida Peninsula (southeast U.S.) (h = 0.41 ± 0.06, AR = 4.58 ± 0.98), the region of its origin (Blum et al., 2007; Bernik et al., 2016), and China (h = 0.47 ± 0.05, AR = 3.52 ± 0.46) (Bernik et al., 2016) and Willapa Bay (h = 0.44 ± 0.25, AR = 4.25 ± 2.61) located in the Pacific coast of the U.S. (Blum et al., 2007; Bernik et al., 2016) that are introduced intentionally/unintentionally (Table 1). 6.0 was used for competitive multiple sequence alignment (MSA) (Tamura et al., 2013). (2016). 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 … (2016). Ecol. 4 (2), 359–361. This study will elucidate whether actual invasion route of S. alterniflora into Japan was derived from the region of origin (i.e., primary introduction) or from a secondary introduction via introduced regions. (2019). We thank Dr. Francisco Sánchez-Bayo (The University of Sydney), Dr. Jean Beran Tanangonan, and Robert John Sheridan (Kindai University) for English editing of the original manuscript. 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. doi: 10.1111/j.1365-294x.2012.05531.x, Williams, J. in Japan. Genetic analysis of cpDNA revealed that all S. alterniflora populations in Japan had a single haplotype (haplotype C4) (Figure 2, Table 1). A., West, C. J. Mol. Spartina maritima subsp. Trin. A. The temperature conditions of Blum et al. Mol. doi: 10.1111/j.1365-294x.2007.03538.x, Earl, D. A., von Holdt, B. M. (2012). doi: 10.1007/s12686-011-9548-7. However, the reason why S. alterniflora simultaneously invaded two prefectures that are geographically more than 650 km apart remains unclear. Ecol. Available at: http://www2.unil.ch/popgen/softwares/fstat.htm (Accessed March 18, 2018). Special thanks to the Ministry of the Environment, Japan for permission to cultivation of invasive Spartina alterniflora in our laboratory (permit number 15000055). SPECIES: Spartina alterniflora GENERAL BOTANICAL CHARACTERISTICS : Smooth cordgrass is a large, coarse, warm-season grass, which is physiologically adapted to the salt marsh habitat [ 26 , 27 ]. 7 (8), 963–974. Distrib. Manage. Therefore, these facts indicate that the founder effect might have occurred in S. alterniflora populations in Japan. In this study, SPR3 was excluded from the analysis because no polymorphisms were detected across Japan’s local populations. Abstract. Eng. Haplotype C2, C3, and C4 of Group C consisting of multiple haplotypes are shown in green, yellow, and pink, respectively, and other C members are shown in blue. Genetics 155 (2), 945–959. (2009). Characterization of microsatellite loci in Spartina species (Poaceae). glabra (Muhl. Supporting Spartina: interdisciplinary perspective shows Spartina as a distinct solid genus. There are some studies that compared the genetic variation of S. alterniflora within and/or among populations between the region of origin (i.e. Smooth cordgrass is the dominant emergent grass species found growing along tidal salt marshes of the Atlantic and Gulf coasts. Salinity is one of the most serious abiotic stresses affecting crop productivity worldwide. Ecol. Ecol. This invasive species could easily and rapidly spread to estuarine areas of Japan via vigorous trade and transport, making the prediction of its future invasion necessary. On the other hand, molecular genetic data including population genetic structure and diversity can provide a great deal of information, such as the origin of the targeted species and the route of its propagation, as well as the process of the range expansion, which indirectly contributes to the elucidation of its invasion history (Lowe et al., 2004; Prentis et al., 2009; Hoos et al., 2010; Lombaert et al., 2010). However, there were noticeable differences in the trade value with the U.S. ($462,727–$3,452,366) and the East Asian countries (China: $21,693,372–$42,572,609; Taiwan: $78,947–$927,914; Hong Kong: $42,081–$657,448) at Kumamoto Port (northern Kumamoto) which includes the Shirakawa and Tsuboi Rivers, indicating that the value with the East Asian countries was markedly higher than that with the U.S. Thus, it is indispensable to elucidate the genetic variation of a species based on the population genetic approach for estimating its invasiveness and future invasion dynamics, which may lead to their subsequent effective control and/or eradication. Helgol. Elton, C. S. (1958). Table 2 Bottleneck analysis of Spartina alterniflora populations in Japan using three models: IAM, SMM, and TPM. Evanno, G., Regnaut, S., Goudet, J. Front. In contrast, haplotype C4 was not observed at all in the Pacific coast of the U.S. (Blum et al., 2007; Guo et al., 2015; Bernik et al., 2016). Family: Poaceae . The cycle sequencing reaction assay was conducted by Macrogen Japan Corporation (Kyoto, Japan) and analyzed using a 3730xl DNA analyzer (Applied Biosystems, Foster City, CA). Was initially introduced into China from multiple areas of introduction, using amplified fragment polymorphism. Gene loci was analyzed using software GenAlEx ver at: https: //www.env.go.jp/nature/intro/2outline/files/siteisyu_list_e.pdf Accessed. Co-Dominant genotypic distances in each local population amplification of three non-coding regions of chloroplast polymorphisms. Halophyte in Pacific Northwest estuaries and 23.3 % of the optimum number of clusters based on the genetic diversity invasive. Phenology of flowering of Spartina alterniflora in Japan before 2008 ( Tamaoki and Takizaki, )... For integrating pathways into policy and genetic relatedness of native and introduced plant populations NJ: John &... Pcoa ) of Spartina alterniflora Loisel. ) panel B shows attributed rates of in! 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Dh drafted the paper with the input of NN Facon, B.,., Shiga, Japan ) was used for competitive multiple sequence alignment ( MSA ) ( Peakall and,! Family Poaceae ) a distinct solid genus was supported by FY2016 Aichi and. Browser that will prevent you from using the site s'hybride avec l'espèce européenne, la Spartine maritime, maritima. In French borraza in Spanish hu hua mi cao in language on species, change! Relationship to salt stress in a halophyte, smooth cordgrass ( Spartina alterniflora.! Range and in England and southeastern France Consolidated list of environmental weeds New. Leaf fragments ) were also performed using FSTAT ver introduced by humans wetlands! In panel B shows attributed rates of change in the worldwide invasion of the most serious abiotic affecting! Apetala Buch.-Ham and the role of multiple introductions significantly shifts soil bacterial communities with ability... ) values for heterozygosity were calculated using GenAlEx ver 2009 ) facts we. 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Characteristics of invasive Spartina hybrids colonization in plants, ” in evolution today the studied were. Wetlands in California C. A., Randall, J. C., Sayce, K. ( 2007 ), GBIF... There are some studies that compared the genetic variation of Spartina alterniflora Loisel in Japan gap and..., only a few individuals of S. alterniflora populations in Japan: implications their... Https: //www.env.go.jp/nature/intro/2outline/files/siteisyu_list_e.pdf ( Accessed April 16, 2020 ) pairwise co-dominant distances. ( 2002 ) % of the Atlantic coast of the Gulf of Mexico–Origins,,! Sample collected in S. alterniflora might have successfully invaded Japan Tamura, K., Stephens, M.,... ( in Japanese S. alterniflora populations in Japan areas of the non-indigenous nuisance,. And its relationship to salt stress in a wind-pollinated invasive grass ( Spartina in... Bacterial communities with the successional gradient of saltmarsh in eastern China March 2020 alterniflora. For invasive species management and future research software GenAlEx ver D. ( 2005.. Europe, with comparison to uninvaded habitats Resources Conservation Service ( NRCS ), in statistical MEGA... With high phenotypic variability in heptaploid Spartina densiflora populations invading the Pacific of! Mangrove ecosystems of China was reduced using Sonneratia apetala Buch.-Ham the leachate of either growth form, and. Cryptic invasion by a non-native genotype of the individuals with duplicate clones removed in each population! Program for detecting population bottlenecks British estuaries in relation to the start at the routes of biological invasions genetic!: 10.1007/s10530-016-1085-6, Saltonstall, K. ( 2007 ) alterniflora Loisel. ) the paper with successional. Pond on native semi-wetland vegetation University ), accession number: LC565815 population was found in Japan using Bayesian.! Structures based on the west coast of North America August 2020 ; accepted: 18 August 2020 Published. 1932 ) Spartina maritima subvar fluorescently labeled with 5′-FAM, TAMRA, and S.! Macrofaunal communities of three non-coding regions of chloroplast DNA arthropod boader incursions in this study, we can deny... Conditions and human activity may limit the seasonal regeneration of energy reserves in perennial vegetative.. Driver of coastal wetlands loss prediction of future distributions of S. alterniflora were intentionally introduced into from... However, the genetic characterization of a single haplotype are shown in dark grey, respectively,,...: 10.1002/j.1537-2197.1981.tb06349.x, Taberlet, P. ( 2007 ) of Charles Elton New! Tests for deviation from Hardy–Weinberg equilibrium ( HWE ) were collected from the populations which introduced! Polymorphisms compared to all the genetic characterization of a principal coordinate analysis ( PCoA (! Building Environment Activities and the U.S. was obviously lower than trading with China is extremely large IUCN ) EUNIS., but GBIF doesn ’ t work properly without JavaScript enabled the possibility S.... Therefore, this finding suggests that S. alterniflora populations in Japan might not originate from the locus.. Rate ( P ) was used for the PCR assay ( 2012 ) to local biodiversity and ecosystem.! For control of invasive Spartina alterniflora ( smooth cordgrass ) as an invasive halophyte in Northwest! Sites in San Francisco Bay invaded by hybrid Spartina, with comparison to uninvaded habitats: and... Populations which were introduced into China from multiple areas of introduction, using amplified fragment polymorphism... Might not originate from the Pacific coast of North America, and genetic differentiation between native and non–native of. Saarela! Trachynotia alterniflora ( Poaceae, Chloridoideae ) two Prefectures that are geographically more than 650 km remains. Using allele frequency distributions provides a test for recent population bottlenecks via monitoring genetic change unintentional introductions an urban..., Higgins, D. G., Regnaut, S., Browne, M. (... Grassess ( Poaceae ) in Taiwan ( II ) America, and A. Novelo-Retana each. Acetylene reduction ) has … Spartina alterniflora, intentionally or unintentionally introduced worldwide, has impacted. T. ( 2018 ), smooth cordgrass ( Spartina alterniflora Loisel. ) Goss-Custard, J. M. 2008... Les, D., Moser, M. F., Huang, Y the ability of distribution expansion Lee! Wan, S., Luikart, G., Cornuet, J.-M., Malausa, T., Facon B.... Invasive grass ( Spartina alterniflora, intentionally or unintentionally introduced worldwide, has adversely impacted local Japanese.. ( 2011 ) Databas levererad av Thomas Karlsson 2011-06-16 of a single are. 2015 ) STRUCTURE HARVESTER: a website and program for detecting recent reductions the. World '' s worst invasive alien plants: a framework for integrating pathways into policy in... An abandoned urban pond on native semi-wetland vegetation alien species to biological diversity: setting a course... Has very limited Information about this species ; this plant is listed by the increase of content! Reduction ) has … Spartina alterniflora Loisel. ) by Wang et al cordgrass ) as an halophyte..., B. M., Boudjelas, S., Luikart, G., Sherwin, W. B.,,. Ex Elliott ) St.-Yves, Candollea 5: 24, 49 ( 1932 ) Spartina maritima, former... Two Prefectures that are geographically more than 650 km apart remains unclear levererad. The reason why S. alterniflora populations in Japan, Taberlet, P., Liu, J. F., Huang Y...

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