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Proceedings of the Third International Conference on Invasive ...

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<str<strong>on</strong>g>Proceedings</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> <str<strong>on</strong>g>Third</str<strong>on</strong>g> <str<strong>on</strong>g>Internati<strong>on</strong>al</str<strong>on</strong>g> <str<strong>on</strong>g>C<strong>on</strong>ference</str<strong>on</strong>g> <strong>on</strong> <strong>Invasive</strong> SpartinaChapter 3: Ecosystem Effects <str<strong>on</strong>g>of</str<strong>on</strong>g> <strong>Invasive</strong> SpartinaSPARTINA ALTERNIFLORA INVASIONS IN THE YANGTZE RIVER ESTUARY,CHINA:ASYNOPSISB. LI 1 ,C-Z.LIAO, X-D. ZHANG, H-L. CHEN,Q.WANG, Z-Y. CHEN, X-J. GAN, J-H. WU,B.ZHAO, Z-J. MA,X-L. CHENG,L-F.JIANG, Y-Q. LUO, AND J-K. CHENCoastal Ecosystems Research Stati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> Yangtze River Estuary, Ministry <str<strong>on</strong>g>of</str<strong>on</strong>g> Educati<strong>on</strong> Key Laboratory for BiodiversityScience and Ecological Engineering, The Institute <str<strong>on</strong>g>of</str<strong>on</strong>g> Biodiversity Science, Fudan University, #220 Handan Road, Shanghai200433, China1 For corresp<strong>on</strong>dence: bool@fudan.edu.cnSpartina alterniflora was first found in <str<strong>on</strong>g>the</str<strong>on</strong>g> Yangtze River estuary in <str<strong>on</strong>g>the</str<strong>on</strong>g> mid 1990s, and has nowbecome <str<strong>on</strong>g>the</str<strong>on</strong>g> most abundant vascular plant in <str<strong>on</strong>g>the</str<strong>on</strong>g> estuarine marshlands. We have investigated <str<strong>on</strong>g>the</str<strong>on</strong>g>potential c<strong>on</strong>sequences <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina alterniflora invasi<strong>on</strong>s to <str<strong>on</strong>g>the</str<strong>on</strong>g> salt marshes <strong>on</strong> two large islands in<str<strong>on</strong>g>the</str<strong>on</strong>g> estuary, Ch<strong>on</strong>gming and Jiuduansha, over <str<strong>on</strong>g>the</str<strong>on</strong>g> past five years, focusing <strong>on</strong> effects <strong>on</strong> biodiversityand ecosystem processes <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> marshlands resulting from <str<strong>on</strong>g>the</str<strong>on</strong>g> invasi<strong>on</strong>. We here summarize <str<strong>on</strong>g>the</str<strong>on</strong>g>major findings from our previous work and provide <str<strong>on</strong>g>the</str<strong>on</strong>g> relevant literature.Keywords: Biodiversity, ecosystem processes, plant invasi<strong>on</strong>s, saltmarshes, Spartina alterniflora,Yangtze River estuaryINTRODUCTIONThe Yangtze River estuary with two nati<strong>on</strong>al naturereserves is an important ecoregi<strong>on</strong> as it is <str<strong>on</strong>g>the</str<strong>on</strong>g> home for manyec<strong>on</strong>omically and ecologically important species, and servesas an important stopover site for migratory birds <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> EastAsian-Australasian Flyway (Chen et al. 2003; Ma et al.2004). However, in comm<strong>on</strong> with o<str<strong>on</strong>g>the</str<strong>on</strong>g>r estuaries in <str<strong>on</strong>g>the</str<strong>on</strong>g>world (Cohen and Carlt<strong>on</strong> 1998; Grosholz 2002), <str<strong>on</strong>g>the</str<strong>on</strong>g>Yangtze River estuary is seriously threatened by exoticspecies invasi<strong>on</strong>s. Of all <str<strong>on</strong>g>the</str<strong>on</strong>g> invasive exotic species, smoothcordgrass (Spartina alterniflora) introduced from NorthAmerica, has become <str<strong>on</strong>g>the</str<strong>on</strong>g> most harmful exotic plant to <str<strong>on</strong>g>the</str<strong>on</strong>g>salt marshes, leading to multifold c<strong>on</strong>sequences to <str<strong>on</strong>g>the</str<strong>on</strong>g>estuary. Over <str<strong>on</strong>g>the</str<strong>on</strong>g> past five years, we have investigated <str<strong>on</strong>g>the</str<strong>on</strong>g>populati<strong>on</strong> spread <str<strong>on</strong>g>of</str<strong>on</strong>g> S. alterniflora <strong>on</strong> two major islands in<str<strong>on</strong>g>the</str<strong>on</strong>g> estuary, Ch<strong>on</strong>gming and Jiuduansha, and examined <str<strong>on</strong>g>the</str<strong>on</strong>g>ecosystem-level effects <str<strong>on</strong>g>of</str<strong>on</strong>g> its invasi<strong>on</strong>. This synopsis isbased <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g>se investigati<strong>on</strong>s. Detailed reports werepublished elsewhere. (See References for <str<strong>on</strong>g>the</str<strong>on</strong>g> full list.)SPREAD AND DISTRIBUTIONS. alterniflora was intenti<strong>on</strong>ally introduced fromAmerica to China in 1979 (An et al. this volume), and was<str<strong>on</strong>g>the</str<strong>on</strong>g>n spread to <str<strong>on</strong>g>the</str<strong>on</strong>g> Yangtze River estuary in <str<strong>on</strong>g>the</str<strong>on</strong>g> mid 1990sboth by natural dispersal and intenti<strong>on</strong>al introducti<strong>on</strong>s. For<str<strong>on</strong>g>the</str<strong>on</strong>g> purposes <str<strong>on</strong>g>of</str<strong>on</strong>g> ecological engineering, i.e., rapid sedimentaccreti<strong>on</strong>, S. alterniflora was <str<strong>on</strong>g>the</str<strong>on</strong>g>n intenti<strong>on</strong>ally introduced totwo large islands in <str<strong>on</strong>g>the</str<strong>on</strong>g> estuary, Jiuduansha (in 1997) andCh<strong>on</strong>gming (in 2001 and 2003). On each island a nati<strong>on</strong>alnature reserve had been set aside for c<strong>on</strong>serving nativebiodiversity and maintaining ecosystem integrity. In fact,this invasive plant has invaded almost all <str<strong>on</strong>g>the</str<strong>on</strong>g> mudflats andsalt marshes in <str<strong>on</strong>g>the</str<strong>on</strong>g> Yangtze River estuary (Fig. 1A), S. alternifloraei<str<strong>on</strong>g>the</str<strong>on</strong>g>r col<strong>on</strong>ized tidal mudflats (Fig. 1D) or replacednative plants like Scirpus mariqueter (Fig. 1E) (Chen et al.2004) and Phragmites australis (Wang et al. 2006b), and hasbecome <strong>on</strong>e <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> most abundant species in estuarineecosystems during a period <str<strong>on</strong>g>of</str<strong>on</strong>g> just over 10 years. Our recentdata obtained through remote sensing show that in 2005 S.alterniflora m<strong>on</strong>ocultures accounted for 49.4% and 37.0% <str<strong>on</strong>g>of</str<strong>on</strong>g><str<strong>on</strong>g>the</str<strong>on</strong>g> vegetated area in D<strong>on</strong>gtan (Fig. 1B) and Jiuduansha (Fig.1C) marshlands respectively (Li et al. 2009). Range expansi<strong>on</strong><str<strong>on</strong>g>of</str<strong>on</strong>g> S. alterniflora still c<strong>on</strong>tinues in estuarine wetlands.Successful invasi<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> S. alterniflora in <str<strong>on</strong>g>the</str<strong>on</strong>g> YangtzeRiver estuary were <str<strong>on</strong>g>the</str<strong>on</strong>g> result <str<strong>on</strong>g>of</str<strong>on</strong>g> interacti<strong>on</strong>s between biotic,abiotic and human factors (Wang et al. 2006a). The “enemyrelease hypo<str<strong>on</strong>g>the</str<strong>on</strong>g>sis” that is used to explain successful invasi<strong>on</strong>s<str<strong>on</strong>g>of</str<strong>on</strong>g> exotic plants elsewhere might also apply to those <str<strong>on</strong>g>of</str<strong>on</strong>g> S.alterniflora in <str<strong>on</strong>g>the</str<strong>on</strong>g> Yangtze River estuary. Spartina alterniflorahas a number <str<strong>on</strong>g>of</str<strong>on</strong>g> superior traits such as fast growth, a highlyefficient use <str<strong>on</strong>g>of</str<strong>on</strong>g> resources, a high tolerance to salt and a welldevelopedbelowground system that make it a superiorcompetitor or invader and a potent ecosystem engineer (Li etal. 2009). It is for this latter reas<strong>on</strong> that S. alterniflora waswidely used for erosi<strong>on</strong> c<strong>on</strong>trol and sediment accreti<strong>on</strong> al<strong>on</strong>gshorelines in <str<strong>on</strong>g>the</str<strong>on</strong>g> Yangtze River estuary (Wang et al. 2006a),which might have directly led to its rapid spread in <str<strong>on</strong>g>the</str<strong>on</strong>g>marshlands. Frequent reclamati<strong>on</strong> in <str<strong>on</strong>g>the</str<strong>on</strong>g> Yangtze Riverestuary has made <str<strong>on</strong>g>the</str<strong>on</strong>g> estuarine ecosystem susceptible to S.alterniflora as areas outside <str<strong>on</strong>g>the</str<strong>on</strong>g> dike exhibit c<strong>on</strong>diti<strong>on</strong>s typical<str<strong>on</strong>g>of</str<strong>on</strong>g> early saltmarsh successi<strong>on</strong>, which favor S. alterniflorara<str<strong>on</strong>g>the</str<strong>on</strong>g>r than native plants. Envir<strong>on</strong>mental changes (saltwaterintrusi<strong>on</strong> and eutrophicati<strong>on</strong>) caused by human activities- 147 -

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