brittingham 1983
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1/6
Have Cowbirds Caused Forest Songbirds to Decline?Author(s): Margaret Clark Brittingham and Stanley A. TempleSource: BioScience, Vol. 33, No. 1 (Jan., 1983), pp. 31-35Published by: Oxford University Presson behalf of the American Institute of Biological SciencesStable URL: http://www.jstor.org/stable/1309241.
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8/10/2019 Brittingham 1983
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H a v e Cowbirds Caused
F o r e s t
Songbirds
o
Decline
Margaret
Clark
Brittingham
and
Stanley
A.
Temple
Brown-headed
cowbird
populations
and
their
rate of brood
parasitism
on forest
songbirds
in eastern
North
America
have increased
since
1900. Brood
parasitism
of
forest
songbirds
is
highest
near
open
habitat.
High
brood
parasitism
rates within
isolated
fragments
of forest habitat reduce
reproductive
success
of certain forest
songbirds
and
may
be
responsible
for their recent declines.
(Accepted for publica-
tion
10
July
1982)
Brood
parasites
lay
their
eggs
in the
nests
of host
species
that hatch
and rear
the
parasite's
young.
Obligate
brood
par-
asites never rear
their
own
young
and
are, therefore,
totally
dependent
on
host
species.
The
brown-headed cowbird
(Molothrus
ater)
is the
only
obligate
brood
parasite
in North America.
Brown-headed
cowbirds
and other
brood
parasites
substantially
reduce the
reproductive
success
of their
hosts;
few-
er than normal or often none of the
host's
young fledge
from a
parasitized
nest
(Payne
1977,
Mayfield
1977a).
In
response
to
this
threat,
many
host
spe-
cies
that coevolved
with
brood
parasites
can reduce the
success of
parasites by
deserting
a
parasitized
nest,
building
a
new nest
floor over the
parasite's eggs,
or
evicting
the
eggs
(Rothstein 1975).
On
the other
hand,
species
that have
not
evolved
with
brood
parasites
almost al-
ways
lack effective defense
mechanisms
and are
extremely
vulnerable
when
they
come
into contact
with brood
parasites
(Mayfield 1965, Rothstein 1975).
There
has
been
recent
concern
over
declining
populations
of
many
forest
song-
birds
in
the
deciduous forest
biome
of
eastern
North America
(Ambuel
and
Tem-
ple
1982,
Temple
and
Temple
1976,
Rob-
bins
1979,
Whitcomb
et
al.
1981),
and it
has
been
suggested
that
intense
brood
parasitism
of
these
naive
hosts
by
brown-
headed
cowbirds,
a
relatively
recent addi-
tion to the avifauna
of
the
biome,
has
played
a role
in the
declines
(Ambuel
and
Temple
1982,
Mayfield
1977a,
Robbins
1979, Whitcomb
et
al.
1981).
We
have
reviewed
the
available
information
on
cowbirds
in the
eastern deciduous
forest
and have identified ecological factors that
determine
the rate of
parasitism
on forest
songbirds.
We have found
temporal,
spa-
tial,
and biogeographic
correlations that
implicate
brood
parasitism
in declines of
forest
songbirds.
CHANGES
N COWBIRD
DISTRIBUTION
ND
ABUNDANCE
Prior
to
the
1800s the brown-headed
cowbird was found
primarily
in the
plains
and
prairies
west of the
Mississip-
pi
River. It was absent from the
large
tracts of unbroken forest that covered
much of eastern North America because
its
feeding
habits and social behavior
restricted
it
to
open
habitat.
As the
east-
ern
forests
were cut
by
settlers and land
was
cleared for
farming,
open
habitat
was
created,
which
provided opportuni-
ties
for
an
eastward
expansion
of the
cowbirds'
range
(Friedmann 1929,
May-
field
1965).
By
the late
1800s,
the cow-
bird was
apparently
widespread
in east-
ern North
America,
but it was
not
abundant
and
was
found
primarily
in
cultivated
areas.
It was
uncommon in
forest habitat
(Bendire
1895,
Friedmann
1929),
and
at that
time,
the
impact
of
cowbird parasitism on the reproductive
success
of
forest songbirds
was
probably
minimal.
In recent
decades
the
cowbird
has
increased
sharply
in
abundance
(Bys-
track
and
Robbins
1977,
Mayfield
1965),
but
its
range
in
eastern North
America
has
probably
not
changed
dramatically.
We examined
regional
Audubon Christ-
mas
bird count
records
from 1900
to
1980
to
document
changes
in
cowbird
abun-
dance in the East within
this
century.
This
method
has
been
used for other
species
(Bock
and
Lepthien
1976a,b).
We examined records for 11 southern
states
(below
370
latitude
from Texas to
the
Atlantic
Ocean)
where most cow-
birds
in the East
migrate
to
spend
the
winter
(Peterson
1980,
Robbins et
al.
1966).
For each
year
we tallied
the
indi-
vidual Christmas
bird
counts
in these
11
states and
calculated
the percentage
of
these counts on
which cowbirds
were
reported.
The
number
of counts
ranged
from 1
in 1900 to
205 in 1980.
Cowbirds
have been
reported
with
increasing
fre-
quency
from
1900
to 1980
(Figure
1),
and
we
interpret
this
as
an indication
that
cowbird numbers have also been steadily
increasing.
This
increase
in
the
abundance of
brown-headed
cowbirds
is most
likely
due
to an
increase
in
their
winter food
supply
and
wintering
habitat.
Waste
grain
in rice
(Oryza
sativa)
fields
in
southern
states
provides
an abundant
source of
food
during
the
winter
months;
this
waste
rice
is the
principal
winter
food
for
several
species
of
blackbirds,
including
the cowbird
(Meanley
1971).
Brittingham
nd
Temple
are
with
the
Department
f
Wildlife
Ecology,
University
of
Wisconsin-Madison,
226 Russell
Laboratories,
630Linden
Drive,
Madi-
son,
WI
53706.
?
1983American nstituteof
Biolog-
ical Sciences. All
rights
reserved.
January
1983
31
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3/6
80
60
o
20
140
-
0
Figure
1. An index
to cowbird abundance
from 1900-1980 taken from
Audubon
Christ-
mas
bird
count records
(r
=
0.961,
P
50%
open.
Our
study
area
contained
more
than 15 such
openings.
We
determined
the location
of nests and
distances
to
openings
by
using compass-
es
and
referring
to aerial
photographs
taken
in October
1980.
We
grouped
nests
into four
categories
depending
on
the distance
from
the nest
to the nearest opening in the forest great-
er than
0.2
ha
in area
(Table
1).
The
percentage
of
parasitized
nests
differed
significantly
among
the four
distance cat-
egories
because
of a decline
in
frequency
of
parasitism
as
distance to
open
habitat
increased.
This decline
does not
appear
to be
the
result
of cowbird's
preference
for
certain host
species
that
nest
only
near
openings.
Rather,
a
similar
array
of
forest-dwelling
songbirds
nested
and
were
parasitized
in
each of
the four
dis-
tance
categories
(Table 2).
The
mean
number of cowbird
eggs per
nest also differed significantly in the four
distance
categories,
but the
mean
num-
bers of
cowbird
eggs per parasitized
nest
did
not
(Table
1).
Therefore,
the decline
in number
of cowbird
eggs per
nest
with
increasing
distance
from
an
opening
is
due to
a decline
in the
percentage
of
nests
parasitized
rather
than to
a lower
number
of
parasitized
nests
with multi-
Table
2. Locations
of
nests
with
respect
to nearest
forest
opening
>
0.02
ha.
Parasitized
nests/total
nests
within
indicated distance from an
opening
Species
0-99
m
100-199
m
200-299
m
?300
m
Acadian
lycatcher
(Empidonax
irescens)
3/8
1/14
1/7
0/8
Least
flycatcher
(Empidonax
minimus)
1/2
0/3
0/0
0/0
Wood
hrush
(Hylocichla
mustelina)
4/6
4/4
1/1
3/4
Veery
(Hylocichla
uscescens)
3/3
0/0
0/1
0/1
Red-eyed
vireo
(Vireo
olivaceus)
0/0
1/1
0/0
0/0
American
redstart
(Setophaga
ruticilla)
0/3
1/1
0/0
0/0
Hooded warbler
(Wilsonia
citrina)
3/3
1/1
0/0
0/0
Mourning
warbler
(Oporornis
hiladelphia)
1/1
0/0
0/0
0/0
Louisiana
waterthrush
(Seiurus
motacilla)
0/0
0/0
0/0
0/1
Ovenbird
(Seiurus
aurocapillus)
5/5
6/8
1/1
0/1
Scarlet
tanager
(Piranga
olivacea)
0/0
1/2
0/0
0/0
Indigo
bunting
(Passerina
cyanea)
6/8
2/2
0/0
0/0
Rose-breasted
rosbeak
(Pheuticus
udovicianus)
0/1
0/1
1/1
0/2
'Arlo
Raim,
University
of
Illinois,
Champaign,
per-
sonal
communication,
October,
1982.
January
1983
33
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5/6
pie
cowbird
eggs.
Since the
rate of
cow-
bird
parasitism
is
a direct
function of
cowbird
density
(McGeen
1972,
May-
field
1977a),
the
decline
in
intensity
of
brood
parasitism
in the
interior of
an
extensive
forest
is in
agreement
with
our
data on cowbird
distribution
(Figure
2).
We also
examined the
influence of
very
small
openings
(-0.01
ha and
-
8/10/2019 Brittingham 1983
6/6
Herik
and the Wisconsin
chapter
of
the
Nature
Conservancy
for
permission
to
work in the Baraboo Hills
study
area.
John
Cary
and
Kurt
Johnson were
valu-
able field assistants. We thank
Stephen
Rothstein for comments on an earlier
draft of this
paper
and the staff and
students of the
Department
of Wildlife
Ecology
for
their
continual advice and
support.
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