Population Trends in Evening Grosbeak |
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Christmas Bird Count data show changes in
The Evening Grosbeak (Coccothraustes vespertinus)
The National Audubon Society's 100-year-old Christmas Bird Count (CBC) is an
excellent tool for tracking such irruptions as well as for monitoring long
term bird population trends.
The CBC is particularly important in tracking birds that breed in remote
regions but that winter in areas
that are more accessible. Since much of the breeding range of the Evening
Grosbeak is inaccessible,
winter surveys like the CBC provide the best indicator of the health of the
species.
For this analysis, we measured Evening Grosbeak abundance obtained from
CBCs between 1959 and 1998.
Not all the counts held during this period were analyzed. Instead, only
counts that occurred during at least half of the
40 years of the analysis period were included. This way, we reduced the
bias resulting from new counts that started
during the later years of the analysis period. To minimize bias due to
varying observer effort, the total number of birds
observed during any CBC was divided by the total party hours for that
count, thereby allowing a standardized birds/party
hour (BPH) comparison. For each year, the average BPH was calculated from
all CBCs that were above 30° latitude. The
annual average BPH was graphed, and a linear regression was calculated in
order to look for indications of continuous
increase or decrease in abundance of grosbeaks over the time period in
question. This same method was also used for
within-state or -province analysis.
The results from the CBC clearly show that the Evening Grosbeak is an
irruptive species across much of North America.
What is apparent is that Evening Grosbeak exhibits a biennial pattern of
irruption (Graph 1); years where they were
plentiful were followed by years when low numbers were reported. When
Evening Grosbeak did irrupt, they invaded different
regions (Figure 1). This is best exhibited by the following animated map
(Figure 1), which shows hot spots of Evening
Grosbeak abundance. Note how the regions where the highest BPH values (gold
coloration) vary from year to year.
time period 59-98 60-79 80-98 60-69 70-79 80-89 90-98 Evening Grosbeak 0.0177 0.2323 * -0.5988 *** 0.0005 -0.0278 -0.0114 -0.747 ***
Graph 1 also shows that Evening Grosbeak numbers were stable or increased
until 1980 when their numbers began to decline significantly. Table 1
shows the results of the regression analysis. The decline of Evening
Grosbeak numbers between 1980 and 1998 was significant (p<0.001) which
indicates that there is less than one chance in one thousand that the
decline in Evening Grosbeak numbers was due to random fluctuations in
abundance.
Table 1 also indicates that the rate of decline has increased between 1990
and 1998. Figure 2 shows which state or province exhibited the most
significant
declines in Evening Grosbeak between 1980 and 1998. What is clear from
Figure 2 is that the Northeast and Great Lakes region show the steepest
declines in Evening Grosbeak numbers. On the other hand, Evening Grosbeak
numbers appear stable in the Rocky Mountain region.
The cause of the decline in Evening Grosbeak numbers is unknown, but there
are several possibilities. The most obvious is that Evening Grosbeaks may
simply not be moving as far south during the winter due to the hemispheric
trend in warmer winter temperatures. The declines might also be related to
food availability. Hardwood tree seeds, a favorite natural source of food
of Evening Grosbeaks, may be less common due to broad-scale changes in
forestry practices in Canada. Finally, Evening Grosbeak numbers in the East
may be stabilizing after their colonization of the north woods east of the
Great Lakes. Prior to the
late nineteenth century, the Evening Grosbeak did not occur east of the
Great Lakes; since then they have expanded rapidly across Ontario,
Michigan, Quebec,
the Canadian Maritimes, and New England.
Whatever the reasons for the decline in Evening Grosbeak numbers, it is
through long term continent-wide citizen-based monitoring projects like the
CBC and Project FeederWatch that the health of wild bird populations can be
assessed. This monitoring can both sound an alarm before the situation
becomes dire as
well as lead to a greater understanding of overall environmental changes
that may be the cause of dramatic changes in bird populations. Another
BirdSource project, the Irruptive Bird Survey, is tracking the abundance of
winter food across the continent, in order to determine whether irruptive
migrants vary their wintering areas by according to natural food abundance.
Thank you to all who have contributed to these important projects. We
encourage you to continue to participate.
Steve Kelling
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