Harbour seals consume more juvenile and adult salmon in estuaries than elsewhere in the Strait of Georgia

Recent studies of harbour seal diets (2012-2014) have been used to estimate the amounts of salmon consumed by seals in the Strait of Georgia. However, these diet data have primarily come from estuary habitats, and may not be representative of all seals. We analysed 1,317 scat samples collected at an...

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Bibliographic Details
Main Authors: Majewski, Sheena, Nordstrom, Chad, Thomas, Austen C., Trites, Andrew W.
Format: Text
Language:English
Published: Western CEDAR 2018
Subjects:
Online Access:https://cedar.wwu.edu/ssec/2018ssec/allsessions/453
https://cedar.wwu.edu/cgi/viewcontent.cgi?article=2888&context=ssec
Description
Summary:Recent studies of harbour seal diets (2012-2014) have been used to estimate the amounts of salmon consumed by seals in the Strait of Georgia. However, these diet data have primarily come from estuary habitats, and may not be representative of all seals. We analysed 1,317 scat samples collected at an estuary (Cowichan Bay) and 7 non-estuary sites from Apr–Nov 2016 and Apr–May 2017 to compare salmon consumption inside and outside of estuaries. Using high-throughput DNA techniques, we determined seals consumed a wide range of prey (n = 238 species)—with gadids (primarily hake) and forage fish (primarily herring) dominating diets in both habitats (typically >75% of diet when combined). Salmonids were consumed throughout the year. Juvenile salmonids (based on life-histories and size of recovered bones) collectively made up 1.4% (CI = 0.8–2.1%) of the spring diet at non-estuaries and 2.5% (CI = 1.4–3.9%) in Cowichan Bay in 2016/17. Primary juvenile salmon consumed were chinook, and to a lesser extent coho and chum. The 1.1% difference between sites is considerable when translated into number of smolts consumed, and indicates smolt predation was 50% higher at our estuary site. Salmon consumption spiked in the fall (driven by returning adult chum salmon), and was much higher in Cowichan Bay (35%, CI = 29–40%) than at non-estuary sites (9.1%, CI = 7.3–11.0%). Furthermore, the bulk of salmon consumed at non-estuary locations was driven by one site (Belle Chain Islets) which appeared to be heavily influenced by Fraser River runs. Our findings highlight that estuaries may not be useful as proxies for non-estuary sites when assessing predation on species of conservation concern (including salmonids) and that models estimating harbour seal related salmon mortality should consider differences in consumption rates inside and outside of estuaries in the Salish Sea.