Seabirds – Sentinel Species of the Gulf, 5th Edition

Seabirds
Status: moderate in 2022
Trend: unchanged since 2005 

 

Prepared by:
Catherine Čapkun-Huot and Jean-François Rail
Canadian Wildlife Service
Environment and Climate Change Canada

Photo of various seabirds like the Common Murre, Razorbill, and Atlantic Puffin.
Copyright information 

Cat. No.: En153-114/2-2025E-PDF   
ISBN:  978-0-660-77179-3  

 

This publication may be reproduced for personal or internal use without permission, provided the source is fully acknowledged. However, reproduction of this publication in whole or in part for purposes of redistribution requires the prior written permission from the Canada Water Agency by contacting:   

Canada Water Agency
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Email:water-eau@cwa-aec.gc.ca

 

© His Majesty the King in Right of Canada, as represented by the President of the Canada Water Agency and the Minister of the Environment and Climate Change, 2025   

Published by authority of the Minister of l’Environnement, de la Lutte contre les changements climatiques, de la Faune et des Parcs du Québec
© Gouvernement du Québec, 2025

 

Aussi disponible en français sous le titre: Les oiseaux de mer – Des espèces sentinelles du golfe, 5e édition

Highlights

Seabirds nesting in the migratory bird sanctuaries of the North Shore are surveyed every five years. Their status is considered “moderate” due to trends observed in five indicator species: the Common Murre and Razorbill are doing very well, the reduced number of Atlantic puffins is increasing, the status of tiny Caspian Tern population remains precarious despite recent growth, and the decline of the American Herring Gull continues. The abundance of food resources, the presence of predators, and human disturbance are key factors at play.

Problem

Following the adoption of the Migratory Birds Convention Act (1917), migratory bird sanctuaries were established in 1925 on the North Shore of the Gulf of St. Lawrence to protect important seabird colonies (Figure 1). Since then, these sanctuaries have been censused approximately every five years. Sixteen seabird species nest there. Among them, five species have been selected as bioindicators of the ecosystem’s state because they use varied feeding strategies and exhibit different levels of vulnerability to human disturbance. For example, the Common Murre, Razorbill, and Atlantic Puffin, belonging to the Alcidae family, dive to feed, while the American Herring Gull (formerly “Herring Gull”) and Caspian tern, from the Laridae family, feed at the surface. However, the Alcidae have different ecological niches: the Razorbill feeds more in coastal areas than the Atlantic Puffin, and the Common Murre dives to much greater depths than the Razorbill and the Atlantic Puffin. Furthermore, the American Herring Gull can be observed in highly anthropized environments, whereas the Caspian tern is sensitive to human disturbance. Monitoring the status and trends of seabird populations in migratory bird sanctuaries provides information on prey abundance, predation, human disturbance and, more generally, the health of the Gulf of St. Lawrence, a rich and diverse ecosystem.

Study area

 

Figure 1: Migratory bird sanctuary 

Map of the nine migratory bird sanctuaries of the North Shore of the Gulf of St. Lawrence
Text description of Figure 1

The nine migratory bird sanctuaries of the North Shore of the Gulf of St. Lawrence are distributed between Sept-Îles and Blanc-Sablon:

  • Corossol Island
  • Betchouane
  • Watshishou
  • Île à la Brume
  • Baie des Loups
  • Sainte-Marie Islands
  • Gros Mécatina
  • Saint-Augustin
  • Brador Bay

Key measures

We assess the status of the breeding populations of five seabird species representative of the Gulf of St. Lawrence, considering short-term trends (since 2010) and long-term trends (since 1982). A variation of less than 25% is considered a relatively stable trend. Population status and rating are determined according to the following criteria:

  • "Good" status and rating of 0: long-term and short-term trends increasing (by 25% or more). 
  • "Moderate-good" status and rating of 1: long-term and short-term trends respectively stable and increasing or increasing and stable. 
  • "Moderate" status and rating of 1: long-term and short-term trends stable, or opposite trends in the long and short term. 
  • "Moderate-poor" status and rating of 1: long-term and short-term trends respectively stable and decreasing (by 25% or more) or decreasing and stable. 
  •  "Poor" status and rating of 2: long-term and short-term decline. 

Additionally, the status and rating of a population with very limited numbers can be adjusted to better reflect its precarious situation, beyond short- and long-term trends. 

Indicator of the sum of the five seabird species representative of the Gulf of St. Lawrence

The sum of the five species' ratings define the overall indicator status (total of  0-1 = good, 2-3 = moderate-good, 4-6 = moderate, 7-8 = moderate-poor, 9-10 = poor). 

Status and trends

The American Herring Gull: a continuing decline

The American Herring Gull population grew steadily in the decades following the creation of the migratory bird sanctuaries (1925). However, the decline of cod and the subsequent Canadian moratorium on groundfish fishing in 1992 had significant impacts on American Herring Gulls, which relied heavily on fish waste discarded at sea by fishers. By 1993, the population had shrunk to 22% of its 1988 size. More recently, the small population, which seemed to have stabilized, has resumed its decline, with a 64% decrease since 2010 (Figure 2). The presence of terrestrial predators (such as red foxes) in certain sanctuaries could partly explain this downward trend. In view of the negative short- and long-term trends observed, the population status is considered “poor.”

Figure 2: Number of American Herring Gulls breeding

Graph of number of American Herring Gulls breeding
Text description of Figure 2

Number of American Herring Gulls breeding in the migratory bird sanctuaries of the North Shore between 1925 and 2022. 

  • 1925: approximately 1,000 individuals
  • 1930: an increase to about 2,500 individuals
  • 1935: a continued rise to 3,300 individuals
  • 1940: 4,500
  • 1945: approximately 5,300
  • 1950: an estimated 4,700 individuals
  • 1955: 6,500
  • 1960: the population grew significantly to about 11,000 breeding individuals 
  • 1965: reached a peak of around 18,000 individuals
  • 1972: about 15,000
  • 1977: a decline to 10,000 
  • 1982: a moderate rise was seen with about 14,500 individuals
  • 1988: a historical peak when the breeding population reached nearly 23,000 individuals
  • 1993: the number of breeders dropped to about 4,800
  • 1998-99: remained stable
  • 2005: the population slightly increased to about 6,000 
  • 2010: remained stable around 6,000
  • 2015: the number of breeding American Herring Gulls declined to about 4,600 individuals
  • 2022: reached approximately 2,300

 

The Caspian Tern: encouraging signs despite precariousness

The only regular nesting site of the Caspian Tern in Québec is in the Île à la Brume Migratory Bird Sanctuary. The Caspian Tern population totalled several dozens breeding pairs between 1925 and 1950, disappeared for the first time in 1950, then reappeared only to quickly decline between 1955 and 1965, reaching very low levels. The population has been struggling for several decades, deserting the Île à la Brume in some years, then reappearing with generally fewer than five pairs (Figure 3). Human disturbance could affect this sensitive species. Nevertheless, the latest survey revealed encouraging signs for the species: four nests were counted at the Île à la Brume, in addition to a fifth in the Saint-Augustin sanctuary, where the last nesting record dated back to 1976. Despite the short- and long-term increase in the population, its small size remains a major concern, which is why its status is considered “moderate-poor.”

 

Figure 3: Number of Caspian Terns breeding

Graph of Caspian Terns breeding
Text description of Figure 3

Number of Caspian Terns breeding in the migratory bird sanctuaries of the North Shore between 1925 and 2022.

  • 1925: the number of breeding Caspian Terns was approximately 60 individuals
  • 1930: to around 90 individuals
  • 1935: about 85 individuals
  • 1940: the breeding population had declined to around 66 individuals
  • 1945: rose to about 90 individuals
  • 1955: the number of breeders was close to 76 individuals
  • 1960: a sharp decline to approximately 44 individuals
  • 1965: the downward trend continued with only about 12 individuals observed
  • 1972: the breeding population dropped further to around 3 individuals
  • 1977: remained extremely low with a similar count
  • 1982: about 8 individuals were recorded
  • 1988: increasing slightly to around 16
  • 1993-2015: the population remained very low, consistently under 10 individuals
  • 2022: there was a modest increase, with the number of breeding Caspian Terns reaching approximately 12 individuals

 

 

The Alcidae: generally positive trends

The Alcidae, once exploited for their eggs, meat, and feathers, have greatly benefited from the Migratory Birds Regulations, resulting from the Migratory Birds Convention Act (adopted in 1917), and the migratory bird sanctuaries of the North Shore established in 1925. The Act prohibits the hunting, harassment and disturbance of migratory bird nests and eggs. Relatively stable between 1925 and 1960, Alcidae populations subsequently plummeted to their lowest levels in the 1970s. Disturbance and poaching in the sanctuaries, facilitated by the popularization of outboard motors, is suspected to be the cause. The increased surveillance of the sanctuaries that followed allowed the populations to recover. Population trends for all three alcid species are generally positive, although they vary from one species to another.

The Common Murre population on the North Shore has experienced rapid growth in recent years. The number of breeding birds has more than doubled since 2010 and nearly quadrupled since 1982 (Figure 4). Despite a marked decline in numbers between 1999 and 2005, there is no doubt that the population status is “good.”

 

Figure 4: Number of Common Murres breeding

Graph of number of Common Murres breeding
Text description of Figure 4

Number of Common Murres breeding in the migratory bird sanctuaries of the North Shore between 1925 and 2022. The data is presented as a bar chart, with the x-axis representing the year and the y-axis showing the number of breeding individuals.

  • 1925: the estimated number of breeding Common Murres was approximately 7,000 individuals
  • 1930: this number increased slightly to about 8,000 
  • 1935: the population had grown to roughly 12,000
  • 1940: it reached around 12,500
  • 1945: the count decreased slightly to approximately 10,000 individuals
  • 1950: the population increased again to about 11,500
  • 1955: population is near 12,000
  • 1960: recorded a similar count of around 11,500 individuals
  • 1965: there was a decline to roughly 7,500
  • 1972: a further decrease to about 6,000
  • 1977: the number had risen again to around 9,000 breeding individuals
  • 1982: the population increased to approximately 14,000
  • 1988: there was a significant rise to about 26,000
  • 1993: the count reached roughly 32,000 and remained relatively steady in 
  • 1998–1999: remained relatively steady at approximately 31,000 individuals
  • 2005: the population had decreased to about 15,000
  • 2010: population climbed back up to roughly 26,000
  • 2015: population was estimated at around 34,000. 
  • 2022: the most dramatic increase with the number of breeding Common Murres reaching an estimated 70,000 individuals

 

The number of Razorbills has risen steadily over the past 40 years, reaching 16 times the number recorded in 1982 (Figure 5). This growth suggests that forage fish are abundant and that conditions in the migratory bird sanctuaries are highly suitable for Razorbill reproduction. Therefore, the population status is also considered “good.”

 

Figure 5: Number of Razorbills breeding

Graph of the number of Razorbills breeding
Text description of Figure 5

This graphic showcases the estimated number of breeding Razorbills recorded across various years from 1925 to 2022. The data is displayed as a bar chart, with the x-axis representing the year and the y-axis showing the number of breeding individuals.

  • 1925: the estimated number of breeding Razorbills was around 10,000 individuals
  • 1930: this number increased to approximately 14,000
  • 1935: the population declined to about 8,000
  • 1940, 1945, and 1950: population values ranging between 8,000 and 9,000 individuals
  • 1955: there was a notable increase to around 19,000 individuals
  • 1960: population slightly declined to about 17,000
  • 1965: 15,000
  • 1972: a sharp decline followed with the population dropping to approximately 6,000 breeding individuals
  • 1977 and 1982: this number remained low, staying around 5,000 to 6,000
  • 1988: the population rose slightly to about 9,000 individuals
  • 1993: 10,000 
  • 1998–1999: the number of breeding Razorbills increased to roughly 14,000
  • 2005: this rose further to about 22,000
  • 2010: the population reached approximately 33,000 individuals
  • 2015: it increased again to around 50,000
  • 2022: the estimated number of breeding Razorbills had grown significantly to approximately 60,000 individuals

 

 

The Atlantic Puffin population shows a stable long-term trend despite fluctuations (an increase of 53% between 1982 and 1993, a decrease of 54% between 1993 and 2010, then an increase of 60% between 2010 and 2022) (Figure 6). The population status is “moderate-good.” The underlying causes of this trend reversal are poorly understood.

 

Figure 6: Number of Atlantic Puffins breeding

Graph of the number of Atlantic Puffins breeding
Text description of Figure 6

This graphic displays the estimated number of breeding Atlantic Puffins recorded at various years from 1925 to 2022. The chart uses bars to show the population count, with the x-axis representing the years and the y-axis indicating the number of breeding individuals.

  • 1925: the number of breeding Atlantic Puffins was approximately 55,000 individuals
  • 1930: 63,000
  • 1935: reached a peak of roughly 72,000 individuals
  • 1940: the population slightly declined to around 66,000
  • 1945: about 60,000 
  • 1950 and 1955: the numbers remained fairly stable with approximately 60,000 to 62,000 breeding individuals
  • 1960: there was a notable decrease to around 23,000 individuals. 
  • 1965: the population rebounded to about 35,000 
  • 1972: declined again to roughly 25,000
  • 1977: the number dropped further to about 15,000 individuals
  • 1982: the population increased to around 30,000
  • 1988: rising slightly to approximately 35,000
  • 1993: peaking again at about 47,000
  • 1998-1999: the population decreased to roughly 29,000 
  • 2005: declined slightly to 25,000 
  • 2010: about 21,000 
  • 2015 onwards: there was a gradual increase, reaching approximately 25,000 individuals
  • 2022: the estimated number of breeding Atlantic Puffins rose to around 35,000
 

Outlook

The population trends of the five indicator species nesting in the migratory bird sanctuaries of the North Shore have remained relatively unchanged: Common Murre and Razorbill populations continue to grow in the short and long term; the Atlantic Puffin population is stable in the long term, although it has shown growth in the short term; the Caspian Tern population is increasing in the short and long term but remains extremely fragile; and the decline in the American Herring Gull population has resumed its course. As a result of these trends, the overall status of the indicator remains “moderate.” The next quinquennial censuses of the migratory bird sanctuaries will enable us to verify whether the trends observed for the different species will continue or be reversed.

For more information

  • Working Group on the State of the St. Lawrence Monitoring. 2024. Overview of the State of the St. Lawrence 2024. St. Lawrence Action Plan. Environment and Climate Change Canada, Ministère de l’Environnement, de la Lutte contre les changements climatiques, de la Faune et des Parcs du Québec, Parks Canada, Fisheries and Oceans Canada, Stratégies Saint-Laurent. 72 pages.
  • Rail, J.-F. 2021. Eighteenth census of seabirds breeding in the sanctuaries of the North Shore of the Gulf of St. Lawrence, 2015. The Canadian Field-Naturalist 135:221–233.
  • Rail, J.-F. and R. Cotter. 2015. Seventeenth census of seabird populations in the sanctuaries of the North Shore of the Gulf of St. Lawrence, 2010. The Canadian Field-Naturalist 129:152–158.
  • Wilhelm, S. I., J.-F. Rail, P. M. Regular, C. Gjerdrum and G. J. Robertson. 2016. Large-scale changes in abundance of breeding Herring Gulls (Larus argentatus) and Great Black-backed Gulls (Larus marinus) relative to reduced fishing activities in southeastern Canada. Waterbirds 39:136–142.
  • Wilhelm, S. L., J.-F. Rail, D. Iles, S. Avery-Gomm and C. M. Francis. 2023. Seabirds. Pages 125–131. State of the Atlantic Ocean synthesis report. Bernier, R.Y., Jamieson, R.E., Kelly, N.E., Lafleur, C. et Moore, A.M. (eds.). Canadian Technical Report of
  • Fisheries and Aquatic Sciences 3544.

State of the St. Lawrence Monitoring Program

Five government partners—Canada Water Agency, Environment and Climate Change Canada, Fisheries and Oceans Canada, Parks Canada, the Ministère de l’Environnement, de la Lutte contre les changements climatiques, de la Faune et des Parcs du Québec—and Stratégies Saint-Laurent, a non-governmental organization that works actively with riverside communities, are pooling their expertise and efforts to provide Canadians with information on the state of the St. Lawrence and the long-term trends affecting it.

 

For more information about the State of the St. Lawrence Monitoring Program, please consult: www.planstlaurent.qc.ca/en/developing-knowledge/state-st-lawrence-monitoring-program

 

Page details

2025-08-14