Geographical Variation and Influencing Factors of <i>Spartina alterniflora</i> Expansion Rate in Coastal China

ZHANG Danhua; HU Yuanman; LIU Miao; CHANG Yu; SUN Lishuang

doi:10.1007/s11769-020-1100-9

Article Contents

Article Navigation > Chinese Geographical Science > 2020 > 30(1): 127-141

ZHANG Danhua, HU Yuanman, LIU Miao, CHANG Yu, SUN Lishuang. Geographical Variation and Influencing Factors of Spartina alterniflora Expansion Rate in Coastal China[J]. Chinese Geographical Science, 2020, 30(1): 127-141. doi: 10.1007/s11769-020-1100-9

Citation:

ZHANG Danhua, HU Yuanman, LIU Miao, CHANG Yu, SUN Lishuang. Geographical Variation and Influencing Factors of Spartina alterniflora Expansion Rate in Coastal China[J]. Chinese Geographical Science, 2020, 30(1): 127-141. doi: 10.1007/s11769-020-1100-9

Geographical Variation and Influencing Factors of Spartina alterniflora Expansion Rate in Coastal China

doi: 10.1007/s11769-020-1100-9

1. School of Transportation Engineering, Shenyang Jianzhu University, Shenyang 110168, China;
2. Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110164, China

Funds:

Under the auspices of Special Foundation for State Major Basic Research Program of China (No. 2013FY111800, 2013FY111100-02)

Received Date: 2019-01-24
Rev Recd Date: 2019-05-07

Abstract

Biological invasion poses a huge threat to ecological security. Spartina alterniflora was introduced into China in 1979, and its arrival corresponded with negative effects on native ecosystems. To explore geographical variation of its expansion rate in coastal China, we selected 43 S. alterniflora sites from Tianjin Coastal New Area to Beihai. The area expansion rate, expansion rate paralleling and vertical to the shoreline were analysed based on Landsat images and field survey in 2015. Simple Ocean Data Assimilation (SODA) and climate data were collected to statistically analyse the influential factors of expansion rate. Results showed that significant difference of S. alterniflora area expansion rate among different latitude zones (P<0.01), increasing from 6.08% at southern (21°N-23°N) to 19.87% in Bohai Bay (37°N-39°N) along latitude gradient. There was a significant difference in expansion rate vertical to shoreline in different latitude zones (P<0.01) with the largest occurring in Bohai Bay (256 m/yr, 37°N-39°N), and showed an decreasing tendency gradually from north to south. No significant difference and latitudinal clines in expansion rate paralleling to shoreline were observed. Expansion rate had significant negative correlation with mean seawater temperature, the lowest seawater temperature, current zonal velocity and meridional velocity and presented a reducing trend as these biotic factors increased; however, they were not significantly correlated with the highest seawater temperature and mean seawater salinity. We identified significant correlations between expansion rate and annual mean temperature, the lowest temperature in January and annual precipitation, but there was little correlation with annual diurnal difference in temperature and the highest temperature in July. The rapid expansion rate in high-latitude China demonstrated a higher risk of potential invasion in the north; dynamic monitoring and control management should be established as soon as possible.
- geographical variation,
- biological invasion,
- Spartina alterniflora,
- expansion rate,
- coastal wetlands,
- China

References

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Geographical Variation and Influencing Factors of Spartina alterniflora Expansion Rate in Coastal China

1. School of Transportation Engineering, Shenyang Jianzhu University, Shenyang 110168, China;

2. Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110164, China

Funds:

Under the auspices of Special Foundation for State Major Basic Research Program of China (No. 2013FY111800, 2013FY111100-02)

Received Date: 2019-01-24

Rev Recd Date: 2019-05-07

Key words:

Abstract: Biological invasion poses a huge threat to ecological security. Spartina alterniflora was introduced into China in 1979, and its arrival corresponded with negative effects on native ecosystems. To explore geographical variation of its expansion rate in coastal China, we selected 43 S. alterniflora sites from Tianjin Coastal New Area to Beihai. The area expansion rate, expansion rate paralleling and vertical to the shoreline were analysed based on Landsat images and field survey in 2015. Simple Ocean Data Assimilation (SODA) and climate data were collected to statistically analyse the influential factors of expansion rate. Results showed that significant difference of S. alterniflora area expansion rate among different latitude zones (P<0.01), increasing from 6.08% at southern (21°N-23°N) to 19.87% in Bohai Bay (37°N-39°N) along latitude gradient. There was a significant difference in expansion rate vertical to shoreline in different latitude zones (P<0.01) with the largest occurring in Bohai Bay (256 m/yr, 37°N-39°N), and showed an decreasing tendency gradually from north to south. No significant difference and latitudinal clines in expansion rate paralleling to shoreline were observed. Expansion rate had significant negative correlation with mean seawater temperature, the lowest seawater temperature, current zonal velocity and meridional velocity and presented a reducing trend as these biotic factors increased; however, they were not significantly correlated with the highest seawater temperature and mean seawater salinity. We identified significant correlations between expansion rate and annual mean temperature, the lowest temperature in January and annual precipitation, but there was little correlation with annual diurnal difference in temperature and the highest temperature in July. The rapid expansion rate in high-latitude China demonstrated a higher risk of potential invasion in the north; dynamic monitoring and control management should be established as soon as possible.

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Reference (76)

[1]	Adams J, Van W E, Riddin T, 2016. First record of Spartina al-terniflora in southern Africa indicates adaptive potential of this saline grass. Biological Invasions, 18(8):2153-2158. doi:10.1007/s10530-015-0957-5
[2]	Adams J B, Grobler, A, Rowe C et al., 2012. Plant traits and spread of the invasive salt marsh grass, Spartina alternilora Loisel., in the Great Brak estuary, South Africa. African Journal of Marine Science, 34(3):313-322. doi:10.2989/1814232x.2012.725279
[3]	Andow D A, Karevia P M, 1993. Spread of invading organisms:patterns of spread. In:Kim K C (ed). Evolution of Insect Pests:Patterns of Variation. New York:Wiley.
[4]	An S Q, Gu B H, Zhou C F et al., 2007. Spartina invasion in China:implications for invasive species management and future research. Weed Research, 47(3):183-191. doi:10.2989/1814232X.2012.725279
[5]	Ayres D R, Zaremba K, Sloop C M et al., 2008. Sexual Repro-duction of Cordgrass Hybrids (Spartina foliosa×Alterniflora) Invading Tidal Marshes in San Francisco Bay. Diversity and Distributions, 14(2):187-195. doi:10.1111/j.1472-4642. 2007.00414.x
[6]	Bancroft J, Smith M T, 2001. Assessing invasion risk using remote sensing. The ESA 2001 Annual Meeting:An Entomological Odyssey of ESA.
[7]	Baumel A, Ainouche M L, Misset M T et al., 2003. Genetic evi-dence for hybridization between the native Spartina maritima and the introduced Spartina alterniflora (Poaceae) in Southwest France:Spartina×neyautii re-examined. Plant Systematics and Evolution, 237(1):87-97. doi:10.1007/s00606-002-0251-8
[8]	Bradley B A, Mustard J F, 2006. Characterizing the landscape dynamics of an invasive plant and risk of invasion using remote sensing. Ecological Application, 16(3):1132-1147. doi:10.1890/1051-0761(2006)016[1132:CTLDOA]2.0.CO;2
[9]	Callaway J C, Josselyn M N, 1992. The introduction and spread of smooth cordgrass (Spartina alterniflora) in south San Francisco Bay. Estuaries, 15(2):218-226. doi:10.2307/1352695
[10]	Campos J A, Herrera M, Biurrun I et al., 2004. The role of alien plants in the natural coastal vegetation in central-northern Spain. Biodiversity Conservation,13(12):2275-2293. doi:10.1023/B:BIOC.0000047902.27442.92
[11]	Cao Haobing, Ge Zhenming, Zhu Zhenchang et al., 2014. The expansion pattern of saltmarshes at Chongming Dongtan and its underlying mechanism. Acta Ecologica Sinica, 34(14):3944-3952. (In Chinese)
[12]	Carton J A, Giese B S, Grodsky S A, 2005. Sea level rise and the warming of the oceans in the Simple Ocean Data Assimilation (SODA) ocean reanalysis. Journal of Geophysical Research:Oceans, 110(C9):C09006.
[13]	Chen H L, Li B, Hu J B et al., 2007. Effects of Spartina alterni-flora invasion on benthic nematode communities in the Yangtze Estuary. Marine Ecology Progress Series, 336:99-110. doi:10.3354/meps336099
[14]	Chen Z Y, Li B, Zhong Y et al., 2004. Local competitive effects of introduced spartina alterniflora on Scirpus mariqueter at Dongtan of Chongming Island, the Yangtze River eatuary and their potential ecological consequences. Hydrobiologia, 528(1):99-106. doi:10.1007/s10750-004-1888-9
[15]	Chung C H, 2006. Forty years of ecological engineering with Spartina plantations in China. Ecol ogical Engineering, 27(1):49-57. doi:10.1016/j.ecoleng.2005.09.012
[16]	Civille J C, Sayce K, Smith S D et al., 2005. Reconstructing a century of Spartina alterniflora invasion with historical records and contemporary remote sensing. Ecoscience, 12(3):330-338. doi:10.2980/i1195-6860-12-3-330.1
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Geographical Variation and Influencing Factors of Spartina alterniflora Expansion Rate in Coastal China

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Geographical Variation and Influencing Factors of Spartina alterniflora Expansion Rate in Coastal China

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Geographical Variation and Influencing Factors of Spartina alterniflora Expansion Rate in Coastal China

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Geographical Variation and Influencing Factors of Spartina alterniflora Expansion Rate in Coastal China

doi: 10.1007/s11769-020-1100-9

1. School of Transportation Engineering, Shenyang Jianzhu University, Shenyang 110168, China; 2. Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110164, China

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1. School of Transportation Engineering, Shenyang Jianzhu University, Shenyang 110168, China;

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