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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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    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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  • 8/10/2019 Brittingham 1983

    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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    http://www.jstor.org/page/info/about/policies/terms.jsphttp://www.jstor.org/page/info/about/policies/terms.jsphttp://www.jstor.org/page/info/about/policies/terms.jsp
  • 8/10/2019 Brittingham 1983

    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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