External Parasite Infestation of Sea-Run Atlantic Salmon (Salmo salar) during Spawning Migration in the Penobscot River, Maine

1999 ◽  
Vol 6 (4) ◽  
pp. 363 ◽  
Author(s):  
Kipp Powell ◽  
Joan G. Trial ◽  
Norman Dube ◽  
Mike Opitz



2010 ◽  
Vol 36 (3) ◽  
pp. 355-365 ◽  
Author(s):  
E. Bombardier ◽  
R. K. Booth ◽  
H. J. Green ◽  
R. S. McKinley


1988 ◽  
Vol 45 (3) ◽  
pp. 568-571 ◽  
Author(s):  
W. A. Montevecchi ◽  
D. K. Cairns ◽  
V. L. Birt

Northern gannets, Sula bassanus, and possibly other seabird species nesting on Funk Island off northeastern Newfoundland preyed on postsmolt Atlantic salmon, Salmo salar. Salmon comprised less than 1% of 2928 regurgitated food samples collected from gannets at the colony. Ten smolt tags were recovered in and near the gannetry during August or September in 1984 through 1986. The tags were from smolts released 3–4 mo earlier in the Penobscot River (Maine) (n = 7) and one each from the Saint John River (New Brunswick) and the Lower Clyde and LaHave rivers (Nova Scotia). These recoveries provide evidence that postsmolt Atlantic salmon from rivers in New England, the Bay of Fundy, and the Atlantic coast of Nova Scotia migrate off eastern Newfoundland This migratory pattern contrasts with that of postsmolts from the Gulf of St. Lawrence, which tend to move northwards along Newfoundland's west coast and through the Strait of Belle Isle.



2009 ◽  
Vol 66 (5) ◽  
pp. 865-870 ◽  
Author(s):  
Rocco C. Cipriano

AbstractCipriano, R. C. 2009. Antibody against infectious salmon anaemia virus among feral Atlantic salmon (Salmo salar). – ICES Journal of Marine Science, 66: 865–870. Archived sera from Atlantic salmon (Salmo salar) that returned to the Penobscot River (Maine), Merrimack River (Massachusetts), and Connecticut River (in Massachusetts) from 1995 to 2002 were analysed for antibodies against infectious salmon anaemia virus (ISAV) using an enzyme-linked immunosorbent assay (ELISA). Up to 60 samples were archived per river system per year. In a given year, the number of fish sampled by ELISA for ISAV antibodies in the Penobscot River ranged from 2.9 to 11.2%, and the range of salmon sampled in the Merrimack River and the Connecticut River was 31.3–100% and 20.0–67.5%, respectively. Archived sera were not available for the 1995 and 2002 year classes from the Connecticut River. In all, 1141 samples were processed; 14 serum samples tested positive for antibodies to ISAV. In the Penobscot River, serum from one fish tested positive in each of the 1995 and 1999 year-class returns, and sera from two fish tested positive in the 1998 returns. In the Merrimack River, sera from four fish tested positive in each of the 1996 and 1997 returns, and sera from two fish were positive in the 2002 return. None of the archived sera from Atlantic salmon that returned to the Connecticut River tested positive.



2015 ◽  
Vol 87 (2) ◽  
pp. 342-359 ◽  
Author(s):  
T. B. Havn ◽  
I. Uglem ◽  
Ø. Solem ◽  
S. J. Cooke ◽  
F. G. Whoriskey ◽  
...  


2005 ◽  
Vol 67 (4) ◽  
pp. 919-930 ◽  
Author(s):  
A. G. Finstad ◽  
F. Okland ◽  
E. B. Thorstad ◽  
T. G. Heggberget


2016 ◽  
Vol 26 (3) ◽  
pp. 347-359 ◽  
Author(s):  
Kristin G. Loughlin ◽  
Keith D. Clarke ◽  
Curtis J. Pennell ◽  
James H. McCarthy ◽  
Brent Sellars


2019 ◽  
Vol 76 (10) ◽  
pp. 1795-1807
Author(s):  
Justin R. Stevens ◽  
John F. Kocik ◽  
Timothy F. Sheehan

Dams challenge Atlantic salmon (Salmo salar) conservation, while hatcheries are a common but poorly evaluated recovery tool. We developed a spatially explicit smolt survival model for the Penobscot River, Maine, USA, population. By partitioning survival through dams (with flow dependency), free-flowing river reaches, and the estuary (with dam dependency), the model quantified how these factors influenced the number of fish entering the ocean. Given historical impounded conditions, 74%–22% of hatchery smolts released entered the ocean annually from 1970 to 2012. Of 19.7 million smolts stocked, 7.7 million entered the ocean (39%). Survival was most variable at dams (range 95% to 63%), followed by in-river (range 98% to 70%) and estuary (range 88% to 82%). Overall, lower-river stocking sites resulted in significantly higher numbers at ocean entry because of fewer dam encounters and shorter migrations. Higher flows also resulted in reduced losses. By reconstructing these freshwater and estuary dynamics, the model provides a more accurate estimate of ocean recruitment annually and can be used for scenario planning of future stocking locations relative to predicted flows while being adaptable to new survival rates.



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