CHRISTOPHER CARTER

Prof. CHRISTOPHER CARTER

orcid

Research Focus & Metrics

Academic Career Length

36Years (1991-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 May 2000 in Aquaculture
Verified
Journal Article
Closed access
CCCHRISTOPHER CARTER
CHRISTOPHER CARTER
RHR.C Hauler
R.C Hauler

1 August 1992 in Journal of Fish Biology
Verified
Journal Article
Closed access
PDF file
IMI. D. Mccarthy
I. D. Mccarthy
CCCHRISTOPHER CARTER
CHRISTOPHER CARTER
DHD. F. Houlihan
D. F. Houlihan

1 August 2003 in Comparative Biochemistry and Physiology Part B: Biochemistry and Molecular Biology
Verified
Journal Article
Closed access
MBMatthew P. Bransden
Matthew P. Bransden
CCCHRISTOPHER CARTER
CHRISTOPHER CARTER
PNPeter D. Nichols
Peter D. Nichols

1 October 2007 in Comparative Biochemistry and Physiology Part A: Molecular & Integrative Physiology
Verified
Journal Article
Closed access
Matthew MillerMatthew Miller
Matthew Miller
PNPeter D. Nichols
Peter D. Nichols
CCCHRISTOPHER CARTER
CHRISTOPHER CARTER

1 December 2008 in Nutrition Research Reviews
Verified
Journal Article
Closed access
Matthew MillerMatthew Miller
Matthew Miller
PNPeter D. Nichols
Peter D. Nichols
CCCHRISTOPHER CARTER
CHRISTOPHER CARTER
The present review examines renewable sources of oils with n-3 long-chain ( ≥ C20) PUFA (n-3 LC-PUFA) as alternatives to oil from wild-caught fish in aquafeeds. Due to the increased demand for and price of wild-caught marine sources of n-3 LC-PUFA-rich oil, their effective and sustainable replacement in aquafeeds is an industry priority, especially because dietary n-3 LC-PUFA from eating fish are known to have health benefits in human beings. The benefits and challenges involved in changing dietary oil in aquaculture are highlighted and four major potential sources of n-3 LC-PUFA for aquafeeds, other than fish oil, are compared. These sources of oil, which contain n-3 LC-PUFA, specifically EPA (20 : 5n-3) and DHA (22 : 6n-3) or precursors to these key essential fatty acids, are: (1) other marine sources of oil; (2) vegetable oils that contain biosynthetic precursors, such as stearidonic acid, which may be used by fish to produce n-3 LC-PUFA; (3) single-cell oil sources of n-3 LC-PUFA; (4) vegetable oils derived from oil-seed crops that have undergone genetic modification to contain n-3 LC-PUFA. The review focuses on Atlantic salmon (Salmo salar L.), because it is the main intensively cultured finfish species and it both uses and stores large amounts of oil, in particular n-3 LC-PUFA, in the flesh.

3 July 2017 in Scientific Reports
Verified
Journal Article
Open access
PDF file
KSKilian M. Stehfest
Kilian M. Stehfest
CCCHRISTOPHER CARTER
CHRISTOPHER CARTER
JMJaime D. McAllister
Jaime D. McAllister
JRJeff D. Ross
Jeff D. Ross
JSJayson M. Semmens
Jayson M. Semmens
Understanding how aquatic species respond to extremes of DO and temperature is crucial for determining how they will be affected by climate change, which is predicted to increasingly expose them to levels beyond their optima. In this study we used novel animal-borne DO, temperature and depth sensors to determine the effect of extremes of DO and temperature on the vertical habitat use of Atlantic salmon Salmo salar in aquaculture cages. Salmon showed a preference for temperatures around 16.5 to 17.5 °C, however, selection of preferred temperatures was trumped by active avoidance of low DO (20.1 °C), which led to a considerable contraction in the available vertical habitat. Despite their avoidance behavior, fish spent a large amount of time in waters with suboptimal DO (<60% saturation). These results show that vertical habitat contraction could likely be a significant consequence of climate change if the reduction in DO outpaces the increase in hypoxia tolerance through local adaptation. They furthermore highlight that site-specific environmental conditions and stock-specific tolerance thresholds may need to be considered when determining stocking densities.