A project of

Swainson's Thrush

The State of Swainson’s Thrushes in the Northeast

Regionally: Declining

Swainson’s Thrush annual population size in the immediate area surrounding all 803 Mountain Birdwatch sampling stations from 2010 to 2024.

The mean (thick, yellow line) annual estimate of Swainson’s Thrush abundance within the immediate area surrounding all 803 Mountain Birdwatch sampling locations, with a 95% Bayesian credible interval (blue polygon, representing estimate uncertainty).

Swainson’s Thrush numbers have likely decreased since Mountain Birdwatch began. Annual fluctuations are evident, but overall counts of this species have steadily declined in the northeastern U.S. over the last half-century. Mountain Birdwatch data indicate an average decline of 2.24% per year in the mountains of our region; this trend equates to a 27.19% decline in population (80% credible interval = -34.77% to -18.85%) between 2010 and 2024.

Predicted Swainson’s Thrush adult density per approximate hectare, as estimated from Mountain Birdwatch data.

Predicted Swainson’s Thrush adult density per approximate hectare in an average year (between 2010 and 2024), as estimated from Mountain Birdwatch data. The base map shows the extent of the Mountain Birdwatch region: eastern New York, Vermont, New Hampshire, and western Maine.

Mean annual population trends and population change (with 80% Bayesian credible intervals [CRI]) for Swainson's Thrush from 2010 through 2024. A red dot indicates strong evidence for a negative trend. An orange dot indicates weak evidence for a negative trend. Strong evidence is suggested for a trend when the 80% CRI does not contain zero. The trend is the annual percentage that a population has (on average) changed each year since 2010, while the population change is the total estimated population percentage change over all years. These estimates have uncertainty, of course, which one can evaluate by examining the credible intervals and the probability that the population has declined probability of decrease) or increased (probability of increase) since 2010.
RegionMean annual
trend (%)
Trend
(80% CRI)
Probability of
decrease
Probability of
increase
Population
change (%)
2010-2024
Population
change (80% CRI)
All regions -2.24(-3.01, -1.48)>0.99<0.01-27.19(-34.77, -18.85)
Maine -1.93(-2.80, -1.05)>0.99<0.01-23.92(-32.81, -13.74)
New Hampshire -2.13(-2.95, -1.31)>0.99<0.01-26.03(-34.26, -16.88)
New York (entire region) -2.89(-3.89, -1.90)>0.99<0.01-33.68(-42.64, -23.58)
New York (Adirondacks only) -3.03(-4.11, -1.97)>0.99<0.01-35.03(-44.40, -24.28)
New York (Catskills only) -1.71(-2.88, -0.45)0.950.05-21.50(-33.53, -6.08)
Vermont -1.98(-2.88, -1.09)>0.99<0.01-24.44(-33.59, -14.17)

Globally: Declining 

Trend estimates from the North American Breeding Bird Survey and eBird largely agree with each other and Mountain Birdwatch data. These data sources indicate modest, widespread declines in Swainson’s Thrush numbers throughout North America (~0.4% per year). These declines appear to have begun in the early 1980s, and are most severe across the northeastern U.S. and southeastern Canada. They have disappeared from many locales, such as coastal areas and major interior valleys, that they once inhabited in California. Counts of this species made at several migratory stopover sites (e.g., Long Point Bird Observatory) have declined as well. Areas where population trends are increasing for Swainson’s Thrush include the the British Columbia coastal forests and Alaska.

State of the Mountain Birds