Abstract
Annual Review of Ecology, Evolution, and Systematics
Vol. 36:
643-689
(Volume publication date December 2005)
(doi:10.1146/annurev.ecolsys.36.102003.152638)
First published online as a Review in Advance on September 9, 2005INTRODUCTION OF NON-NATIVE OYSTERS: Ecosystem Effects and Restoration Implications Jennifer L. Ruesink,1 Hunter S. Lenihan,2 Alan C. Trimble,1 Kimberly W. Heiman,3 Fiorenza Micheli,3 James E. Byers,4 and Matthew C. Kay21Department of Biology, University of Washington, Seattle, Washington 98195-1800; email: ruesink@u.washington.edu, trimblea@u.washington.edu 2Bren School of Environmental Science and Management, University of California, Santa Barbara, California 93106-5131; email: lenihan@bren.ucsb.edu, kay@lifesci.ucsb.edu 3Hopkins Marine Station, Stanford University, Pacific Grove, California 93950-3094; email: micheli@stanford.edu, heiman@stanford.edu 4Department of Zoology, University of New Hampshire, Durham, New Hampshire 03824-2617; email: jebyers@unh.edu ▪ Abstract Oysters have been introduced worldwide to 73 countries, but the ecological consequences of the introductions are not fully understood. Economically, introduced oysters compose a majority of oyster harvests in many areas. Oysters are ecosystem engineers that influence many ecological processes, such as maintenance of biodiversity, population and food web dynamics, and nutrient cycling. Consequently, both their loss, through interaction of overharvest, habitat degradation, disease, poor water quality, and detrimental species interactions, and their gain, through introductions, can cause complex changes in coastal ecosystems. Introductions can greatly enhance oyster population abundance and production, as well as populations of associated native species. However, introduced oysters are also vectors for non-native species, including disease-causing organisms. Thus, substantial population, community, and habitat changes have accompanied new oysters. In contrast, ecosystem-level consequences of oyster introductions, such as impacts on flow patterns, sediment and nutrient dynamics, and native bioengineering species, are not well understood. Ecological risk assessments for future introductions must emphasize probabilities of establishment, spread, and impacts on vulnerable species, communities, and ecosystem properties. Many characteristics of oysters lead to predictions that they would be successful, high-impact members of recipient ecosystems. This conclusion leaves open the discussion of whether such impacts are desirable in terms of restoration of coastal ecosystems, especially where restoration of native oysters is possible. Ultrastructural comparison of the spermatozoa of the Pacific oyster Crassostrea gigas inhabiting polluted and relatively clean areas in Taiwan Aquatic Ecology 43(2):513-519 (2009) Mapping cumulative human impacts to California Current marine ecosystems Conservation Letters 2(3):138-148 (2009) Crassostrea gigas in natural oyster banks in southern Brazil Biological Invasions (2009) Diversity, conservation status and threats to native oysters (Ostreidae) around the Atlantic and Caribbean coasts of South America Aquatic Conservation: Marine and Freshwater Ecosystems 19(3):344-353 (2009) Infestation of the cupped oysters Crassostrea angulata, C. gigas and their first-generation hybrids by the copepod Myicola ostreae: differences in susceptibility and host response Parasitology 136(05):537 (2009)
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