Population structure and ecology of wild Crassostrea gigas (Thunberg, 1793) on the south coast of England
Population structure and ecology of wild Crassostrea gigas (Thunberg, 1793) on the south coast of England
Crassostrea gigas (Thunberg, 1793) is native to Japan and Korea, but has achieved global distribution through human mediated dispersal pathways and natural larval dispersal. Considerable variation in recruitment to wild aggregations has been seen regionally across the globe. Wild recruitment of C. gigas in England has increased in frequency since the millennia however a detailed understanding of their occurrence is limited to an area within the Thames estuary. There have been no English studies to date that reveal how C. gigas interacts with recipient ecosystems, or what impacts winter conditions have. Furthermore conclusive evidence has yet to be presented that feral C. gigas in England are self-sustaining.
Intertidal surveys found substrate type and shore height to have the greatest impact on the locality and abundance of C. gigas recruitment. Gametogenesis initiated in C. gigas when water temperatures increased above 9.5 °C. Maturity was generally reached in the summer, however spawning differed between locations. Wild, intertidal C. gigas were found to spawn twice in a single reproductive season. Initially, spawning was triggered through tidally induced temperature shocking as water temperatures increased above 18 °C. It is thought that the second spawning was triggered by a combination of warm water (+18 °C) and an increase in phytoplankton abundance. Farmed, subtidal C. gigas spawned once, coinciding with the 2nd spawning of intertidal oysters. Rapid growth rates allow a size refuge from the greatest predation pressure to be achieved before growth rates decline over winter. In particular Carcinus maenas is capable of predating C. gigas with a shell length of up to at least 50 mm.
Winter conditions experienced in England are typically colder than those experienced with in the native range of C. gigas, and as such, were detrimental to C. gigas. Juvenile oysters with 4 ± 0.5 mg (dry flesh weight) had significantly higher respiration rates than 6 and 9 ± 0.5 mg juvenile oysters at water temperatures of 7 °C. Temperatures within the pallial cavity of adult C. gigas remained similar to the ambient environment, changing rapidly with tidal immersion/emersion. Furthermore pallial temperatures below 0 °C were recorded and found to reduce gaping activity. Juvenile oysters are the most vulnerable to cold temperatures and are likely affected most years, however only particularly cold years with extensive frosts impacted on adults.
This study expands the base-line knowledge of C. gigas distribution in England to include Southampton Water and Poole Harbour, and investigates the impacts that annual water temperatures and predation have on reproduction and recruitment. The accumulated knowledge and information will enable a better understanding of how establishing C. gigas is likely to develop in the future, and has the potential for use in predictive models and other conservation tools.
Mills, Stephanie Rachael Anne
1c6dafb3-79c3-4628-9937-6dc2a6382bcd
July 2016
Mills, Stephanie Rachael Anne
1c6dafb3-79c3-4628-9937-6dc2a6382bcd
Mills, Stephanie Rachael Anne
(2016)
Population structure and ecology of wild Crassostrea gigas (Thunberg, 1793) on the south coast of England.
University of Southampton, Doctoral Thesis, 231pp.
Record type:
Thesis
(Doctoral)
Abstract
Crassostrea gigas (Thunberg, 1793) is native to Japan and Korea, but has achieved global distribution through human mediated dispersal pathways and natural larval dispersal. Considerable variation in recruitment to wild aggregations has been seen regionally across the globe. Wild recruitment of C. gigas in England has increased in frequency since the millennia however a detailed understanding of their occurrence is limited to an area within the Thames estuary. There have been no English studies to date that reveal how C. gigas interacts with recipient ecosystems, or what impacts winter conditions have. Furthermore conclusive evidence has yet to be presented that feral C. gigas in England are self-sustaining.
Intertidal surveys found substrate type and shore height to have the greatest impact on the locality and abundance of C. gigas recruitment. Gametogenesis initiated in C. gigas when water temperatures increased above 9.5 °C. Maturity was generally reached in the summer, however spawning differed between locations. Wild, intertidal C. gigas were found to spawn twice in a single reproductive season. Initially, spawning was triggered through tidally induced temperature shocking as water temperatures increased above 18 °C. It is thought that the second spawning was triggered by a combination of warm water (+18 °C) and an increase in phytoplankton abundance. Farmed, subtidal C. gigas spawned once, coinciding with the 2nd spawning of intertidal oysters. Rapid growth rates allow a size refuge from the greatest predation pressure to be achieved before growth rates decline over winter. In particular Carcinus maenas is capable of predating C. gigas with a shell length of up to at least 50 mm.
Winter conditions experienced in England are typically colder than those experienced with in the native range of C. gigas, and as such, were detrimental to C. gigas. Juvenile oysters with 4 ± 0.5 mg (dry flesh weight) had significantly higher respiration rates than 6 and 9 ± 0.5 mg juvenile oysters at water temperatures of 7 °C. Temperatures within the pallial cavity of adult C. gigas remained similar to the ambient environment, changing rapidly with tidal immersion/emersion. Furthermore pallial temperatures below 0 °C were recorded and found to reduce gaping activity. Juvenile oysters are the most vulnerable to cold temperatures and are likely affected most years, however only particularly cold years with extensive frosts impacted on adults.
This study expands the base-line knowledge of C. gigas distribution in England to include Southampton Water and Poole Harbour, and investigates the impacts that annual water temperatures and predation have on reproduction and recruitment. The accumulated knowledge and information will enable a better understanding of how establishing C. gigas is likely to develop in the future, and has the potential for use in predictive models and other conservation tools.
Text
Deane, Steffanie (Mills)Thesis
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Published date: July 2016
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Local EPrints ID: 412556
URI: http://eprints.soton.ac.uk/id/eprint/412556
PURE UUID: dff37e16-fc3d-4444-8885-cf2f0099f8b1
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Date deposited: 20 Jul 2017 16:31
Last modified: 15 Mar 2024 15:18
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Author:
Stephanie Rachael Anne Mills
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