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. 2017 Apr;48(4):1525-1537.
doi: 10.1111/are.12988.

Growth, morphometrics, and nutrient content of farmed eastern oysters, Crassostrea virginica (Gmelin), in New Hampshire, USA

Affiliations

Growth, morphometrics, and nutrient content of farmed eastern oysters, Crassostrea virginica (Gmelin), in New Hampshire, USA

R E Grizzle et al. Aquac Res. 2017 Apr.

Abstract

When harvested, oysters represent a removal from the ecosystem of nutrients such as nitrogen (N) and carbon (C). A number of factors potentially affect nutrient content, but a quantitative understanding across the geographic range of the eastern oysters is lacking. The present study was designed to quantify the relationships among various metrics of farmed eastern oysters near its northern geographic range focusing on nutrient content. Hatchery-reared oysters were deployed in polyethylene bags at six sites, and were measured on multiple occasions from 2010-2012. A quadratic polynomial fit to the combined datasets for shell height indicated that on average a 'cocktail' size oyster (63 mm shell height) would be reached after 2 yr, and 'regular' size (76 mm) would require 3 yr. There were significant differences in growth rates and oyster nutrient content among the sites; means for %N in soft tissue ranged from 6.9 to 8.6, and 0.07 to 0.18 in shell. Percent N in soft tissue and shell were highest at two sites at the mouths of rivers with elevated dissolved inorganic N concentrations in the water. Grand means (all sites, seasons and years combined) of soft tissue N and C for regular size oysters were 7.3% and 38.5%, respectively; and for shell N and C were 0.13% and 12.0%, respectively. Our study extends the range of data on nutrient content of the eastern oyster to northern New England, and indicates that oyster size, seasonality, and nutrient concentration in ambient water potentially affect %N and %C content of oysters.

Keywords: bioextraction; eutrophication; nutrient assimilation; shellfish aquaculture; water quality.

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Figures

Fig.1
Fig.1
Six sites where oysters were deployed 2010-2012 (see text for details).
Fig. 2
Fig. 2
Oyster growth as shell height using combined datasets from all sites, seasons, size classes. The gray shaded area around the fit line is 95% confidence interval. Open squares = small size class; Black inverted triangles = large size class.
Fig. 3
Fig. 3
Final shell heights (2.3 yrs of growth) by size class for four sites (no final data were available for BMY and SQR) with complete datasets. P values shown for overall ANOVAs by size class and significance groups based on Tukey test (p<0.05) indicated with lower case letters (normal font for small size class, italicized for large class).
Fig. 4
Fig. 4
Relationship between shell height and whole oyster wet (fresh) weight for overall dataset (all sites, seasons and size classes combined). Best-fit power regression model shown.
Fig. 5
Fig. 5
Relationship between shell height and soft tissue DW for overall dataset (all sites, seasons and size classes combined). Best-fit power regression model shown.
Fig. 6
Fig. 6
Relationship between shell height and shell DW for overall dataset (all sites, seasons and size classes combined Best-fit 2nd order polynomial regression model shown.
Fig. 7
Fig. 7
Relationship between shell height and soft tissue %N from overall dataset (all years, sites, seasons). Best-fit 2nd order polynomial regression model shown.
Fig. 8
Fig. 8
Relationship between soft tissue DW and soft tissue %N from overall dataset (all years, sites, seasons); linear model shown only for those individuals = or > 0.5 g DW.
Fig. 9
Fig. 9
Soft tissue %N and %C by site using combined data from all years and seasons. P values shown are for an ANOVA testing the effect of site. Letters indicate significance among means (Tukeys).
Fig. 10
Fig. 10
Shell %N and %C by site; note: shell data were only available for Nov 2012 sampling (see Table 1). P values shown for overall ANOVAs, etc. as in Fig. 9.

References

    1. Boesch D. Challenges and opportunities for science in reducing nutrient over-enrichment of coastal ecosystems. Estuaries. 2002;25:744–758.
    1. Bricker SB, Wicks C, Woerner J. Effects of nutrient enrichment in the nation’s estuaries: a decade of change. Harmful Algae. 2008;8:21–32.
    1. Bricker SB, Rice KC, Bricker OP., III From headwaters to coast: influence of human activities on water quality of the Potomac River estuary. Aquatic Geochemistry. 2014 doi: 10.10007/s10498-014-9226-y. - DOI
    1. Bricker SB, Ferreira JG, Zhu C, Rose JM, Galimany E, Wikfors G, Saurel C, Miller RL, Wands J, Trowbridge P, Grizzle R, Wellman K, Rheault R, Steinberg J, Jacob A, Davenport E, Ayvazian S, Tedesco M. An Ecosystem Services Assessment using bioextraction technologies for removal of nitrogen and other substances in Long Island Sound and the Great Bay/Piscataqua Region Estuaries. National Oceanic and Atmospheric Administration, National Centers for Coastal Ocean Science; Silver Spring, MD: United States Environmental Protection Agency, Office of Research and Development, Atlantic Ecology Division; Narragansett, RI: 2015. (NCCOS Coastal Ocean Program Decision Analysis Series No. 194). 220 pp + 3 appendices.
    1. Brown BL, Butt AJ, Shelton SW, Paynter KT. Growth and mortality of North Carolina-heritage oysters, Crassostrea virginica, in North Carolina and Chesapeake Bay. Journal of Applied Aquaculture. 1998;8:25–39.

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