We studied foraging ecology of Prothonotary Warblers (Protonotaria citrea) over four breeding seasons to determine if this species exhibited sex-specific or temporal variation in foraging behavior. Significant differences between sexes during the prenestling period were found for foraging height and substrate height (foraging method, plant species/substrate, perch diameter, horizontal location from trunk, and prey location were not significantly different). During the nestling period, this divergence between sexes was evident for foraging height, substrate height, substrate/tree species, and prey location. Additionally, male warblers significantly altered their behavior for all seven foraging variables between the two periods, whereas females exhibited changes similar to those of males for five of the foraging variables. This parallel shift suggests a strong behavioral response by both sexes to proximate factors (such as vegetation structure, and prey abundance and distribution) that varied throughout the breeding season. Sex-specific foraging behavior during the prenestling period was best explained by differences in reproductive responsibilities rather than by the theory of inter-sexual competition for limited resources. During the nestling period, neither hypothesis by itself explained foraging divergences adequately. However, when integrated with the temporal responses of the warblers to changes in prey availability, reproductive responsibilities seemed to be of primary importance in explaining intersexual niche partitioning during the nestling period. We emphasize the importance of considering both intersexual and intraseasonal variation when quantifying a species' foraging ecology. Received 29 September 1988, accepted 16 August 1989.
Department of Zoology, University of Arkansas, Fayetteville, Arkansas 72701 USA,
2348 Church Street, Doylestown, Ohio 44230 USA, and
3U.S. Fish and Wildlife Service, Patuxent Wildlife Research Center,
Laurel, Maryland 20708 USA
SEX-SPECIFIC spatial and behavioral differ-
ences in exploiting food resources have been
documented for woodpeckers (e.g. Selander
1966, Kisiel 1972, Grubb 1975, Jenkins 1979),
emberizids (Morse 1968, Robbins 1971, Wil-
liamson 1971, Franzreb 1983, Holmes 1986),
fringillids (e.g. Ebenman and Nilsson 1982), and
sittids (e.g. McEllin 1979). Two hypotheses have
been advanced to explain intersexual partition-
ing of foraging niches. One is reduction in com-
petition for food resources (Selander 1966, Rob-
bins 1971) and a second correlates other sex-
related behaviors during the breeding season
(e.g. females forage closer to the nest, whereas
males forage higher near singing posts [Morse
1968, Williamson 1971]).
4 Present address: U.S. Fish and Wildlife Service,
North Carolina Cooperative Fish and Wildlife Re-
search Unit, Box 7617, North Carolina State Univer-
sity, Raleigh, North Carolina 27695 USA.
Most studies of foraging behavior during the
breeding season did not consider temporal vari-
ation in niche characteristics; instead, they re-
garded the entire breeding season as a homo-
geneous unit (e.g. Ligon 1968, Morse 1968,
Williams 1975, Hooper and Lennartz 1981,
Franzreb 1983). Due to seasonal changes in hab-
itats (e.g. Whitmore 1979), variation in prey
abundance or distribution (Custer and Pitelka
1978, Jamieson et al. 1982, Craig 1984, Holmes
and Schultz 1988), and changes in reproductive
responsibilities, important information may be
lost if foraging behavior is pooled over a pro-
longed period. For example, foraging behavior
of American Redstarts (Setophaga ruticilla) varies
between the nestling and prenestling stages of
the breeding season (Sherry 1979). Yet, despite
valuable insight into factors influencing avian
foraging ecology that intraseasonal variation
may yield, this aspect of bird foraging behavior
has been largely neglected (but see Root 1967,
Morse 1968, Williamson 1971, Robinson 1986).
During four breeding seasons, we observed
the foraging behavior of male and female Pro-
thonotary Warblers (Protonotaria citrea). Pro-
thonotary Warblers are long-distance migrants
that arrive in Tennessee during early to mid-
April. These cavity-nesting wood-warblers se-
lect nest sites 1-5 m above ground always in
close proximity to water (Petit 1989). Most war-
biers we studied nested in nest boxes (1-2 m
above ground or water) placed along a river
(Petit et al. 1987, Petit 1989). Here we document
the partitioning of breeding territories during
foraging bouts. We divided our data set into
two time periods when changing proximate
conditions might place contrasting demands on
foraging. Measures of niche breadth and over-
lap between sexes and between time periods
were used to discuss intersexual microhabitat
partitioning with respect to predictions of niche
theory.
STUDY AREA AND METHODS
We studied Prothonotary Warblers in riverine hab-
itat along a 30-kra stretch of the Tennessee River
(Kentucky Lake) near New Johnsonville, Benton, and
Humphreys counties, Tennessee. The lake is ca. 2.4
kra in width and is bordered by gently roiling, often
steep, wooded terrain. The riverine habitat, limited
to narrow (10-75 m) bands along the river, is partially
flooded in spring and summer, and is dominated by
willow (Salix sp.), American elm (Ulmus americana),
river birch (Betula nigra), hackberry ( Celtis occidentalis),
sweetgum (Liquidambar styracifiua), maples (Acer spp.),
and buttonbush (Cephalanthus occidentalis). Canopy
height ranges from 6-20 m (œ 12 m), and there is
relatively sparse understory. All trees and shrubs be-
gin to leaf by early April, and most leaves are com-
pletely developed by early May. The river is dotted
with numerous small (0.5-8 ha) islands that are par-
tially flooded in the spring and summer months. The
vegetation there is similar to that of the shoreline.
We observed Prothonotary Warblers on islands and
along the shoreline during the four breeding seasons
between 1984-1987. Foraging observations were di-
vided into prenestling and nestling periods which
corresponded to different adult activities. The pre-
nestling period represented a time of territory estab-
lishment, pair formation, nest building, and incuba-
tion. Observations during this stage were made from
21 April to 3 May 1984, 17 April to 9 May 1985, 11
April to 8 May 1986, and 18 April to 9 May 1987.
Records during the nestling interval included only
those for warbler pairs that were feeding nestlings.
Observations during the nestling phase were made
from 11 June to 23 July 1984, 18 May to 14 July 1985,
and ! June to 18 July 1987. We did not record foraging
data on adults feeding nestlings in 1986.
The seven variables recorded for each observation
of an actively foraging bird are as follows:
1. Foraging method--glean, hover, hawk (for descrip-
tions, see Robinson and Holmes 1984, D. Petit et
al. 1990);
2. Foraging height--for analysis, grouped into the fol-
lowing categories: ---1.0 m, >1.0-3.0 m, >3.0-5.0
m, >5.0-7.0 m, >7.0 m;
3. Perch diameter---1.O cra, >1.0-2.5 cm, >2.5-8.0
cm, >8.0-15.0 cm, >15.0 cm;
4. Substrate--plant species (maple, buttonbush, vine,
willow, elm, hackberry, herbaceous plants, sweet-
gum, birch, miscellaneous bushes, miscellaneous
trees) or substrate (dead branch on ground, snag)
toward which individual directed foraging mo-
tion;
5. Substrate height--same as foraging height (2);
6. Horizontal location from trunk--inner (including
trunk), middle 1/3, outer 1/3;
7. Prey location--leaf, branch, trunk, ground, air.
Sample sizes differed slightly in some analyses be-
cause of our inability to accurately estimate all vari-
ables for some observations. Although we did not
restrict the time of sampling foraging behavior of
Prothonotary Warblers, most (>75%) of our data
were collected before 1200.
Each day, observations were collected on individ-
uals at :>l-rain intervals for up to 10 observations/
individual. Because individuals were often lost from
sight for several minutes, observation periods on an
individual often lasted up to 0.5 h. We ceased re-
cording foraging data when the focal bird was not
seen for more than several minutes or engaged in a
behavior other than foraging. Because Prothonotary
Warblers make ca. 4-12 attempts/rain at capturing
prey while foraging actively, our records do not re-
flect consecutive foraging movements but regular
sampling out of strings of 100 or more foraging ma-
neuvers. Although the :> 1-rain interval between rec-
ords may have allowed adequate time for an individ-
ual to perform statistically independent maneuvers
(cf. Wiens et al. 1970), taking sequential observations
from the same bird and subjecting those data to sta-
tistical analyses may lead to pseudoreplication (Hurl-
bert 1984). However, multiple observations per in-
dividual apparently are better for detection of
uncommon foraging behavior as compared with sin-
gle observations of individuals (Wagner 1981, Mor-
rison 1984, Morrison and With 1987, Holmes and Rob-
inson 1988). To resolve this dilemma, we present
graphically results that reflect all foraging acts ob-
served, but we based statistical analyses upon only
one observation (the first) per individual each day
(e.g. Holmes and Robinson 1988). (Individual identity
was based on unique combinations of colored leg
bands or affinity to a certain territory.) This produced
only one observation per bird each year for >80% of
the individuals, and we believe that we have ade-
quately met the assumption of independence of sam-
ples required for statistical inference.
Because our "populations" of interest were males
and females during each time period regardless of
year, we pooled all 4 years of data for analysis. Annual
variation in Prothonotary Warbler foraging ecology
is presented elsewhere (L. Petit et al. 1990).
Log-likelihood ratio (G) tests (Zar 1974) were used
to test for significant differences in foraging behavior
between the sexes and within each sex between pe-
riods. When possible, adjacent or biologically mean-
ingful cells in contingency tables were collapsed to
ensure that <20% of the cells had expected values of
< 5 (Siegel 1956). Significant differences in mean for-
aging heights were assessed with t-tests.
Niche breadth of each foraging variable (all obser-
vations included) was calculated as: 1/B = p,2, where
B was the niche breadth for a given variable and p,
was the proportion of observations where the birds
were exploiting resource category i (Levins 1968). We
compensated for the varying number of categories
for each foraging variable by standardizing each B so
that it represented the fraction of the largest possible
niche breadth (Reynolds and Meslow 1984). To assess
the degree of resource overlap between sexes, we
used Schoener's (1968) index of niche overlap: Oxy = 1
- 0.5 [ px, - Py, I, where p, and py, were the proportions
of a given foraging behavior (i) utilized by females
(x) and males (y), respectively. Values of Oxy range
from 0 to 1, where 1 represents complete overlap
between the sexes for a given variable, and 0 indicates
complete separation. We made four sets of compari-
sons: (1) males vs. females during the prenestling
period, (2) males vs. females during the nestling pe-
riod, (3) males, prenestling vs. nestling period, and
(4) females, prenestling vs. nestling period.
Arthropod abundance.--We assessed relative arthro-
pod abundance only in 1985 and 1987. Data from
those 2 yr, along with sampling in 1988 and 1989,
suggest that relative arthropod densities follow a sim-
ilar seasonal trend from year to year on our study
areas (but see below). Thus, the data reflect typical
spring and summer temporal changes in arthropod
abundances. Only 1984 was atypical, due to a severe
flood in early May. The effect was to delay emergences
of insects by 2-3 weeks. Our subjective impression
was that once the floodwaters had receded, normal
numbers of insects occupied the bottomland forests.
We can summarize our arthropod sampling for 1985
and 1987-1989 to provide quantitative information
on the interseasonal changes in arthropod numbers.
These changes can be related to concurrent alterations
in the foraging behavior of the warblers.
Every 2 weeks (a "count"), usually from late April
to mid-July, we counted visually arthropods on leaves
1.5-3 m above ground. We searched 20,000 cm 2 of leaf
area (top and bottom) from up to six different tree
species in each sampling plot (5-m radius circle). The
number of leaves searched for each tree species was
proportional to its density within the plot and in-
versely related to its average leaf area. Sixteen plots,
all over water or within 30 m of the river's edge, were
counted over a 2-3-day period. All arthropods were
identified to order. In addition, for each sample plot,
20 sweeps of an insect net were made at each of four
locations. In 1985, data were collected in a slightly
different--but comparable--fashion. This methodo-
logical difference, however, should not be detrimen-
tal to the present analysis because of our standard-
ization of data within years (see below).
Arthropod data for each 2-week period (all 16 plots
summed) are presented as percent deviations from
that year's average number of individuals per count.
In this way, we controlled for between-year differ-
ences in absolute abundances of arthropods. Taxo-
nomic groups are analyzed separately. Data are pre-
sented only for Diptera (flies), Ephemeroptera
(mayflies), Arachnida (spiders), and Lepidoptera lar-
vae (moths and butterflies), because those are the main
prey items of Prothonotary Warblers throughout the
breeding season (L. Petit unpubl.).
RESULTS
A total of 2,978 observations were collected
on foraging "prenestling" male (1,393 obser-
vations), "prenestling" female (579), "nestling"
male (630), and "nestling" female (376) adult
Prothonotary Warblers. For statistical analyses,
we used only one observation per individual
each day, which resulted in sample sizes of 223
(males; n = 147 different individuals) and 101
(females; n = 79 individuals) during the pre-
nestling phase, and 130 (males; n = 87 individ-
uals) and 109 (females; n = 83 individuals) dur-
ing the nestling period.
Prenestling period: males vs. females.--During
spring, before full leaf, male and female war-
biers differed significantly in 2 of the 7 foraging
variables. Males (œ + SD = 3.0 + 3.3 m) foraged
higher than females (œ = 1.5 + 1.9 m; t = 4.3,
df = 321, P < 0.001). Females spent two thirds
of their foraging time below 1 m; males spent
only about half of the time below ! m (G = 20.8,
df = 3, P < 0.001; Fig. 1). Females used shorter
trees and shrubs than did males (G = 11.6, df =
4, P < 0.05; Fig. 2). Males most frequently for-
aged in trees >7 m tall; females often used
shrubs and trees <3 m tall. Intermediate-sized
trees (>3-7 m) were uncommon and were used
<20% of the time by each sex.
The remaining five foraging variables mea-
sured did not differ significantly between male
MALE 601 MALE
60
I-- ' PRE-NESTLING ß PRE-NESTLING
z
uJ [] NESTLING r 40 [] NL
0 40
20 20
I I I
^ ^
FORAGING HEIGHT (m)
Fig. 1. Percentage use of foraging-height intervals
by adult Prothonotary Warblers during prenestling
and nestling periods (see text), 1984-1987.
and female warblers. During the prenestling
period, both sexes captured nearly all prey by
gleaning arthropods from substrates (G = 1.2,
df = 1, P > 0.20; Fig. 3). Small- (-<1.0 cm) and
intermediate-sized (> 1.0-2.6 cm) branches were
used as perch substrates ca. 50% of the time (G
= 4.9, df = 4, P > 0.30; Fig. 4). Use of substrate
also did not vary between sexes during the
prenestling period (G = 2.2, df = 9, P > 0.20;
Fig. 5). Both males and females used a wide
variety of plants but concentrated on willows,
buttonbushes, maples, and dead fallen branch-
es. Both sexes foraged more often in the inner
one third and outer one third of trees and shrubs
than in the middle one third (G = 0.6, df = 2,
P > 0.70; Fig. 6). Use of inner parts of trees and
shrubs was related to the birds' gleaning from
trunks during the early part of the breeding
season. Use of distal regions of trees reflected
typical foraging on emerging leaves and small
twigs. Both sexes attempted to capture most prey
on branches, but they also located prey often
on emerging leaves, trunks, and ground (G =
3.0, df = 3, P > 0.30; Fig. 7).
Nestling period: males vs. females.--Foraging be-
A A A
SUBSTRATE HEIGHT (m)
Fig. 2. Percentage use of plants (substrates) of dif-
ferent heights by adult Prothonotary Warblers during
prenestling and nestling periods (see text), 1984-1987.
havior during the nestling period differed sig-
nificantly between sexes for four variables.
Nearly two thirds of foraging maneuvers by
females (œ = 2.7 _+ 3.0 m) were at 3 m or lower,
whereas males (œ = 4.8 _+ 3.5 m; t = 5.0, df =
234, P < 0.001) spent only 40% of the foraging
time at this level (G = 23.7, df = 3, P < 0.001;
Fig. 1). Male and female warblers feeding nest-
lings differed significantly in use of substrates
(G = 26.2, df = 9, P < 0.01; Fig. 5). Males used
willows and maples more frequently than fe-
males used them, but females foraged more often
on buttonbushes and fallen dead branches than
males did. Females searched for prey in trees
and shrubs smaller than those used by males (G
= 25.2, df = 4, P < 0.001; Fig. 2). During the
nestling period, both sexes foraged most often
on leaves, but males used relatively more leaves
and less branches than females did (G = 4.4,
df = 3, P < 0.01; Fig. 7).
Sexes displayed similar behavior in their
methods of prey capture (G = 7.2, df = 1, P >
0.20; Fig. 3). Gleaning during the summer pe-
riod accounted for >75% of all foraging ma-
neuvers. Both sexes most frequently used
perches <- 1.0 cm (G = 0.2, df = 2, P > 0.90; Fig.
80
I.-- 60
z
n- 40
20
MALE
80
ß PRE-NESTLING
[] NESTLING
I.-- 60
z
n- 40
20
MALE
ß PRE-NESTLING
[] NESTLING
I,-,-
z
ILl
o
n-
ILl
80
60
40
20
FEMALE
GLEAN HOVER HAWK
Fig. 3. Percentage use of foraging methods by adult
Prothonotary Warblers during prenestling and nest-
ling periods (see text), 1984-1987.
4) and used middle and outer parts of bushes
and trees during the nestling period (G = 1.4,
df = 4, P > 0.40; Fig. 6).
Foraging height, substrate type, substrate
height, and prey location differed significantly
between the sexes for one or both periods. The
divergence in substrate type and, correspond-
ingly, substrate height may be an indirect re-
suit of the heights at which male and female
Prothonotary Warblers foraged, and not a direct
outcome of ecological constraints placed on
them. For example, males, which searched for
food at greater heights, did not have access to
lower substrates, such as shrubs and fallen
branches. Similarly, females, which foraged
lower than males, had limited foraging oppor-
tunities in the upper portions of larger trees.
During the prenestling period, males and fe-
males separated on the basis of height, inde-
pendent of substrate type (see above). To de-
termine if males and females partitioned the
use of substrates during the nestling period (in-
I.-- 60
z
n- 40
FEMALE
A A A
PERCH DIAMETER (cm)
Fig. 4. Percentage use of perches of different di-
ameters by adult Prothonotary Warblers during
prenestling and nestling periods (see text), 1984-1987.
dependent of their height differences), we held
foraging height interval constant and applied
G-tests to contingency tables of sex x substrate
for each of three height intervals separately (the
-<1 m and >1-3 m intervals were pooled be-
cause of small sample sizes). There were no sig-
nificant sex-specific differences in use of sub-
strates at any of the foraging-height intervals
(-<3 m: G = 5.8, df = 6, P > 0.40; >3-7 m: G =
1.4, df = 3, P > 0.70; >7 m: G = 0.3, df = 3, P
> 0.90). Conversely, it is possible that substrate
influenced the height at which birds foraged
during the nestling period. A similar analysis
was performed, except that substrate (willow,
maple, and sweetgum) was held constant, and
the distribution of heights for each sex was of
interest. There were no intersexual differences
in the vertical use of maple (G = 1.2, df = 2, P
> 0.50), willow (G = 0.4, df = 1, P > 0.50), or
sweetgum (G = 0.5, df = 1, P > 0.40), although
in each case there was a trend for females to
forage lower than males.
MALE
) ß PRE-NESTLING
[] NESTLING
5
25 - FEMALE
5
0 m o z o m w
o w o z z w
w m z 0
Fig. 5. Percentage use of substrates by foraging adult Prothonotary
nestling periods (see text), 1984-1987.
Warblers during prenestling and
These same analyses were applied to explain
the divergence between sexes in prey location
(i.e. because of varied opportunities encoun-
tered at different heights, males and females
could differ in behavior simply because of their
disproportionate exploitation of those height
intervals). "Prenestling" male and female war-
biers partitioned the vertical component of the
habitat independent of changes in prey location
(see above). We compared locations from which
the sexes attempted to capture prey during the
nestling period with height held constant. Male
and female warblers differed in their use of prey
locations for only 1 of the 4 comparisons across
foraging height intervals; females took prey
from branches more often than males did when
foraging below 1 m (<1 m: G = 16.0, df = 2, P
< 0.001; >1-3 m: G = 0.1, df = 2, P > 0.90; >3-
7m:G= 0.5, df= 2, P > 0.80; >7m:G= 0.5,
df = 1, P > 0.40). Again, these results show no
systematic partitioning of prey locations across
height intervals. When, however, the vertical
distribution of the sexes was analyzed sepa-
rately for each of two categories of prey location
(sample sizes were too small for other cate-
gories), there was a clear trend for males and
females to forage at different heights even when
capturing prey from the same type of micro-
substrate (leaf: G = 10.2, df = 3, P < 0.05; branch:
G = 14.2, df = 2, P < 0.01). We suggest that the
heights at which male and female warblers for-
aged affected the proportion of time each sex
searched for prey on leaves and branches.
Differences between prenestling and nestling pe-
riods.--Throughout the breeding cycle, male
Prothonotary Warblers significantly altered for-
aging tactics for all 7 variables. During the
prenestling stage, males spent <28% of their
time foraging above 3 m, but males feeding
nestlings searched for food 60% of the time
above that height (G = 33.5, df = 3, P < 0.001;
Fig. 1). On average, males feeding nestlings
searched for food nearly 2 m higher than during
the prenestling stage (t = 4.9, df = 348, P <
0.001). Compared with "prenestling" males,
"nestling" males reduced use of branches,
trunks, and ground, and they increased their
maneuvers for prey on leaves and in the air (G
= 55.1, df = 3, P < 0.001; Fig. 7). Males also
changed the tree species upon which they for-
o 4O
MALE
I-INESTLING
8o 1
}-- 60
z
n- 40
MALE
ß PRE-NESTLING
[] NESTLING
I--
z
ILl
o
rr
ILl
O-
FEMALE
INNER MID OUT
Fig. 6. Percentage use of horizontal tree and shrub
axis (inner, middle, outer one third) by adult Pro-
thonotary Warblers during prenestling and nestling
periods (see text), 1984-1987.
aged (G = 37.2, df = 6, P < 0.001; Fig. 5). After
full leaf, males devoted >40% of foraging bouts
to searching in willows and maples, and reduced
use of buttonbushes, vines, and fallen branches.
They also shifted to taller trees (G = 19.8, df =
3, P < 0.001; Fig. 2). Although they still used
gleaning as the most frequent foraging maneu-
ver, males hovered and hawked more often as
the season progressed (G = 9.3, df = 1, P < 0.01;
Fig. 3). "Nestling" males perched on smaller
diameter substrates more than did males earlier
in the season (G = 20.9, df = 3, P < 0.001; Fig.
4). This reflected a preference for perching on
twigs and nearly complete elimination of trunks
as perch sites. During late spring and summer,
males spent less time foraging in the inner por-
tion of trees and shrubs, and more time in the
outer two thirds of the flora (G = 22.0, df = 2,
P < 0.001; Fig. 6).
As the season progressed, females signifi-
cantly changed their foraging behavior for 4 of
the 7 variables. Like male warblers, females for-
aged at greater heights while feeding young,
yet they only occasionally searched above 5 m
(G = 12.5, df = 3, P < 0.01; Fig. 1). On average,
females during the nestling period foraged 1.2
m higher than females during the prenestling
period (t = 3.3, df = 207, P < 0.01). Females
60
I--
Z
ILl
o 40
2o
FEMALE
< o z z
LU Z
..J < rr 0
Fig. 7. Percentage use of prey locations by adult
Prothonotary Warblers during prenestling and nest-
ling periods (see text), 1984-1987.
feeding nestlings increased their use of arthro-
pods on leaves and in flight, while they dimin-
ished search time on the ground, branches, and
tree trunks (G = 15.3, df = 3, P < 0.01; Fig. 7).
They also perched on smaller diameter branch-
es and twigs during the nestling period (G =
6.0, df = 2, P = 0.05; Fig. 4) and spent more time
hovering and hawking insects (G = 5.5, df = 1,
P < 0.05; Fig. 3). Although females increased
their foraging activity on sweetgum, maples,
and other trees, and reduced their use of vines,
buttonbushes, shrubs, and fallen branches dur-
ing the nestling period, the change was not
significant (G = 8.0, df = 6, P > 0.20; Fig. 5).
Female Prothonotary Warblers selected similar
sized trees and shrubs during the prenestling
and nestling periods (G = 2.4, df = 3, P > 0.40;
Fig. 2). Females shifted their foraging patterns
from the inner one third of trees to the center
and outer portions, but this difference was not
quite statistically significant (G = 5.6, df = 2, P
= 0.06; Fig. 6).
Niche breadth.--"Prenestling" male and fe-
TABLE 1. Standardized niche-breadth values for male and female Prothonotary Warblers during the prenest-
ling and nestling periods (see text), 1984-1987.
Foraging Perch Substrate Distance Prey
Period method Height diameter Substrate height to trunk location
Prenestling
Males 0.099 0.425 0.499 0.561 0.633 0.901 0.565
Females 0.073 0.260 0.414 0.586 0.575 0.843 0.578
Nestling
Males 0.280 0.956 0.186 0.466 0.429 0.632 0.189
Females 0.300 0.747 0.172 0.672 0.681 0.761 0.303
male warblers generally had similar standard-
ized niche breadths for each of the seven vari-
ables (difference [g + SD] = 14.9 + 13.4%). Males
had wider niche breadths for 5 of the 7 variables
(Table 1). Birds feeding young had wider niche
breadths (mean difference = 22.6 + 13.0%). In
contrast to "prenestling" birds, niche widths of
females were larger than those of males in 5 of
7 cases during the nestling period. However,
neither of the above two comparisons was sig-
nificantly different (Wilcoxon matched-pairs
signed-ranks test; prenestling: T = 3, P > 0.10;
nestling: T = 7, P > 0.50).
Comparing prenestling and nestling periods,
male and female warblers generally changed
niche breadth in the same "direction" for a giv-
en variable (5 of 7 cases). Both sexes expanded
use of foraging method and height, and con-
tracted niche breadths for perch diameter, prey
location, and distance from trunk. "Nestling"
females increased (and males decreased) diver-
sity of use for both feeding substrates and sub-
strate heights as compared with birds during
the prenestling period.
Niche overlap.--"Prenestling" male and fe-
male warblers demonstrated a high degree of
overlap for all foraging variables (Table 2). Most
(5 of 7) of the overlap indices decreased from
the prenestling period (mean overlap [Oxy] =
0.915 + 0.044) to the nestling period (mean
overlap [Oxy] = 0.881 + 0.085), although this
trend was not statistically significant (Wilcoxon
matched-pairs signed-ranks test, T = 7, P >
0.50). Predictably, niche overlap values usually
were lowest for those variables that were sta-
tistically distinguishable between the sexes.
Arthropod abundance.--All arthropod groups
had initially low relative abundances in April,
peaked between mid-May and late June, and
either declined or remained relatively constant
thereafter (Fig. 8). Emergences of may flies and,
to a lesser degree, dipterans were very distinc-
tive and pronounced. On the other hand, those
of lepidopteran larvae and spiders exhibited
gradual increases and declines with more pro-
longed durations.
DISCUSSION
Intersexual niche partitioning may be the re-
sult of several factors. We considered two pos-
sibilities that may explain the sex-specific for-
aging patterns of male and female Prothonotary
Warblers. First, birds forage at locations which
coincide with an individual's reproductive du-
ties during the breeding cycle. Second, birds
forage in a way to reduce intersexual compe-
tition for food resources.
Reproductive responsibilities.--Sex-specific for-
aging behavior has been associated with activ-
ities during the breeding season. For example,
females stay closer to nests and males stay near-
TABLE 2. Niche overlap values for male and female Prothonotary Warblers during prenestling and nestling
periods (see text), 1984-1987.
Foraging Perch Substrate Distance Prey
Period method Height diameter Substrate height to trunk location
Prenestling 0.975 0.890 0.924 0.853 0.877 0.957 0.932
Nestling 0.988 0.759 0.972 0.847 0.799 0.916 0.884
L
lOO
> o
n- -100
o
u_ 100
z
o
( o
c:) -lOO
DIPTERA
EPHEMEROPTERA
LEPIDOPTERA
LARVAE
ARACHNIDA
..a >- >- w w >-
n- < <Z Z--
Fig. 8. Relative abundances (represented by percent deviations from average for each year) of arthropods
sampled along the Tennessee River in 1985 and 1987-1989. Vertical bars represent + 1 SD. These four taxa
represent the most common prey items eaten by Prothonotary Warblers.
er to singing posts (Morse 1968, Franzfeb 1983).
Prothonotary Warblers partitioned their habitat
vertically and, as predicted by the reproductive
responsibilities theory, males foraged higher
than females. During both periods, males main-
tained territorial vigilance from relatively high
perches. It is unclear, however, whether or not
height preferences were related totally to sex-
specific behaviors associated with the repro-
ductive cycle. First, males foraged at greater
heights during the nestling phase than during
territorial acquisition and courtship. This was
counter to the idea that males forage near their
singing posts, which were high relative to nest
heights during the prenestling period. Activity
during the nestling phase was concentrated at
the relatively low nest site. During the prenest-
ling period, males selected potential nest cav-
ities (1-2.5 m high), placed nesting material in
some of them, and courted females that foraged
close to the ground. This made up <20% of the
males' time (L. Petit unpubl.). Although it ap-
pears that foraging sites of males were influ-
enced to some extent by the presence of females
and the need to locate nest sites, the reproduc-
tive responsibilities theory does not account
fully for the presence of males at such relatively
low heights during the prenestling period. Sec-
ond, female Prothonotary Warblers foraged
lower when building nests. Material for nests
is found near the ground, and gathering nesting
material may have influenced foraging heights
of females during this time. Females foraged
farther (on a vertical scale) from the nest (mean
nest height 1.5 m) during the nestling period,
thereby potentially increasing energetic costs.
In addition, males foraged farther (on a vertical
scale) from the nest while feeding nestlings even
though the sexes shared equally in feeding du-
ties (L. Petit unpubl.). The proposed advantage
to foraging near centers of sex-specific activities
is that time and energy costs are reduced (Morse
1968). Although that did not appear to be the
case during the nestling period, variation in
abundance and distribution of prey may make
it more efficient energetically to forage in areas
of high prey abundance (e.g. higher in trees),
even though those areas are farther from the
nest (see below).
There were some sex-specific preferences for
substrate, substrate height, and prey location,
and those differences appeared to be influenced
by the height at which each sex foraged. In
general, sex-specific height preferences may
have limited the opportunities for both sexes
with respect to other foraging variables (cf. Rob-
inson and Holmes 1984, Holmes 1986). This still
does not explain the preference of males and
females for certain height intervals while for-
aging. Reproductive responsibilities appear to
have influenced foraging height and may be
the primary cause of intersexual niche parti-
tioning, but this hypothesis by itself cannot ex-
plain all facets of sex-specific foraging ecology
that we observed.
Reduction of intersexual competition.--Inter-
sexual habitat partitioning is often accom-
panied by sex-specific variation in morphology
(Selander 1966, Wallace 1974, Austin 1976, Wil-
liams 1980). A 5-10% difference in morpholog-
ical characteristics is typical of sexually dimor-
phic species, although this divergence is
frequently greater (Amadon 1959). In Protho-
notary Warblers, we found males were slightly
larger statistically for culmen length, tarsus
length, wing chord (all <5% difference), and
primary length (6% difference, n > 300 for
each sex; L. Petit unpubl.). Because the differ-
ences in body parts were small, sexual dimor-
phism does not appear to be a pertinent factor
driving the divergence of foraging behavior.
One function of the observed sex-specific for-
aging patterns may be a reduction in competi-
tion between mates. Because competition is dif-
ficult to demonstrate without controlled
experimental manipulations (Wiens 1983), one
must often rely on indirect evidence to assess
ecological principles in nature.
Under conditions of limited resources, indi-
viduals of a population are predicted to "com-
press" niches (MacArthur and Wilson 1967,
Schoener 1974). Similarly, Selander (1966) sug-
gested that intersexual niche partitioning should
occur during periods when resources become
limiting. Although the food supply was greater
during the nestling than the prenestling period
of our study (Fig. 8), it is generally believed
that adults must increase their rate of prey cap-
ture severalfold to meet the increased demand
of growing nestlings (e.g. Walsberg 1983,
Holmes et al. 1986). If we assume a more de-
manding (i.e. competitive) situation for adults
that feed young (as compared with adults dur-
ing the prenestling period), then competition
theory predicts both compressed niches and de-
creased resource overlap between sexes (Se-
lander 1966, Schoener 1974). Niche breadth de-
creased in only 8 of 14 comparisons (57%) from
prenestling to nestling. Although niche overlap
decreased for 5 of the 7 foraging variables (71%)
as the season progressed, most differences were
slight (range = 0.006-0.131). Ricklefs and Lau
(1980) demonstrated that overlap indices must
differ by at least 0.1-0.2 to be statistically dis-
tinct. Thus, our results are equivocal with re-
spect to competition theory. In addition, when
we controlled for sex-specific foraging heights
(see Results), sexes did not systematically par-
tition microhabitat, which would be expected
if intersexual competition was of primary im-
portance. There is little support for the idea that
sexes partition habitat so as to prevent depletion
of resources on a microhabitat scale (cf. Charnov
1976).
Resource abundance and distribution.--Seasonal
shifts in foraging behavior have been attributed
to changes in habitat structure and prey distri-
bution (e.g. Ligon 1973, Austin 1976, Winkler
1979, Morrison and With 1987). However, few
investigators have considered modification of
avian foraging behavior within a season (but see
Root 1967, Sherry 1979, Robinson 1986). We
found in Prothonotary Warblers that both leaf-
ing of vegetation and emergence of insects ac-
counted for at least some of the parallel shifts
in male and female foraging behavior during
4o
2o
w I A
A A
FORAGING HEIGHT(m)
Fig. 9. Percentage use of (A) foraging heights, (B) prey locations, and (C) foraging methods by male (solid
bars) and female (open bars) Prothonotary Warblers not feeding nestlings during the "nestling" period (see
text), 1984-1987.
the breeding season. The contracted summer
niche breadths were related to decreased use of
larger trunks and branches, and increased use
of small branches and twigs in the outer regions
of tree and shrub crowns where there are more
leaves and more food items. Foraging height
niche breadths for both sexes expanded during
the nestling period because of the escalated use
of taller tree species by males. During the nest-
ling period, Prothonotary Warblers hovered
frequently to capture lepidopteran larvae on
the bottom side of leaves. Larvae were substan-
tially more abundant during the nestling pe-
riod than during the prenestling period (Fig.
8). Emergences of mayflies and mosquitos dur-
ing the nestling periods of all years (Fig. 8)
required more diversified foraging maneuvers.
These latter two observations suggest a direct
relationship between prey abundance and for-
aging behavior (also see Holmes and Schultz
1988). Williamson (1971) reported a similar trend
in foraging techniques for Red-eyed Vireos
(Vireo olivaceus) and attributed it to the types
and numbers of arthropods present. Alterna-
tively, Root (1967) showed that the foraging
behavior of Blue-gray Gnatcatchers (Polioptila
caerulea) was more closely related to reproduc-
tive duties than to characteristics of the prey
bas. We have little data on birds in the nestling
period that did not feed nestlings (often as a
result of nest predation). Our observations on
males (n = 101) and females (n = 59), as well as
numerous casual observations over 6 yr, indi-
cate that the abundance and distribution of ar-
thropods were the factors of primary influence
on the foraging ecology during the nestling
period (Fig. 9). Birds that did not feed young
during the summer foraged in ways more sim-
ilar to adults that feed nestlings than to prenest-
ling adults.
We believe that the full leating of foliage and
elevated numbers of arthropods on those leaves
can be linked causally to the significant tem-
poral shifts in foraging ecology of the warblers.
The reproductive responsibilities theory failed
to explain the divergences from centers of ac-
tivity (i.e. nest sites) during the nestling phase
for the same reasons. There should be an in-
verse relationship between foraging efficiency
and distance from centers of activity related to
reproductive duties only if environmental fac-
tors remain relatively constant as distances from
those centers increase (Schoener 1971). Changes
in the benefits accrued at increasing distances
alter that simple, direct relationship. We sug-
gest that a substantial increase in the arthropod
prey created more profitable foraging in the
canopies of trees as compared with fallen
branches, small shrubs, tree trunks, and the
ground exploited by warblers during the
prenestling period. The temporal shift in for-
aging behavior may have been especially crit-
ical to parent birds that fed nestlings. Although
both male and female warblers altered their be-
havior in a parallel fashion, they maintained
distinct height preferences, apparently in re-
lation to their respective reproductive duties.
Those height differences presented males and
females with distinct opportunities to exploit
their foraging environment and may have been
the primary cause of other observed aspects of
intersexual niche partitioning.
ACKNOWLEDGMENTS
This study was funded by the Association of Field
Ornithologists (Bergstrom Award); the American Or-
nithologists' Union (Carnes Award); Sigma Xi, Ar-
kansas Audubon Society Trust Fund; Department of
Biological Sciences, Bowling Green State University;
Department of Zoology, University of Arkansas (all
to L. J. Petit); U.S. Fish and Wildlife Service; and,
especiallyß R. E. and J. M. Petit, and B. E. and K. G.
Reichhardt. Logistical support and equipment were
generously donated by F. M. Stephen, University of
Arkansas; E. Nobleß T. Burrus, and the staff of Nathan
Bedford Forrest State Historic Areaß Tennessee; M.
Gudlin, W. Phifer, and R. Hatcherß Tennessee Wild-
life Resources Agency; W. J. Davis and R. Carlton,
Lambuth Collegeß Jackson, Tennessee; H. Webberß
Lakeshore Methodist Assembly, Eva, Tennessee; and
J. Gentry, University Museum, University of Arkan-
sas. Milk cartons for nest boxes were generously do-
nated by D. Steiner of Smith's Dairy, Orrville, Ohioß
and by C. Goldtrap of Acee Dairyß Fort Smithß Ar-
kansas. P. H. Albers, R. M. Erwin, C. E. Grue, A. K.
Miles-Iversonß D. K. Niven, K. G. Smith, and an anon-
ymous reviewer provided thorough critiques of pre-
vious drafts. This paper is dedicated to the memory
of Richard E. Petit.
LITERATURE CITED
AMADON, D. 1959. The significance of sexual di-
morphism in size among birds. Proc. Am. Phil.
Soc. 103: 531-536.
AUSTIN, G.T. 1976. Sexual and seasonal differences
in foraging of Ladder-backed Woodpeckers. Con-
dor 78: 317-323.
CHARNOV, E. L. 1976. Optimal foraging: attack strat-
egy of a mantid. Am. Nat. 110: 141-151.
CRmG, R.J. 1984. Comparative foraging ecology of
Louisiana and Northern waterthrushes. Wilson
Bull. 96: 173-183.
CUSTER, T. W., & F. A. PITELKA. 1978. Seasonal trends
in summer diet of the Lapland Longspur near
Barrowß Alaska. Condor 80: 295-301.
EBENMAN, B., & S. G. NILSSON. 1982. Components of
niche width in a territorial bird species: habitat
utilization in males and females of the Chaffinch
(Fringilla coelebs) on islands and mainland. Am.
Nat. 119: 331-344.
FR.NZREn, K.E. 1983. Intersexual habitat partition-
ing in Yellow-rumped Warblers during the
breeding season. Wilson Bull. 95: 581-590.
GRUBB, T. C., JR. 1975. Weather-dependent foraging
behavior of some birds in a deciduous woodland.
Condor 77: 175-182.
HOLMES, R.T. 1986. Foraging patterns of forest birds:
male-female differences. Wilson Bull. 98: 196-
213.
, & S. K. ROBINSON. 1988. Spatial patterns,
foraging tactics, and diets of ground-foraging
birds in a northern hardwoods forest. Wilson Bull.
100: 377-394.
., & J. C. SCHULTZ. 1988. Food availability for
forest birds: effects of prey distribution and abun-
dance on bird foraging. Can. J. Zool. 66: 720-728.
ß T. W. SHERRY, & F. W. STURGES. 1986. Bird
community dynamics in a temperate deciduous
forest: long-term trends at Hubbard Brook. Ecol.
Monogr. 56: 201-220.
HOOPER, R. G., & M. R. LENNARTZ. 1981. Foraging
behavior of the Red-cockaded Woodpecker in
South Carolina. Auk 98: 321-334.
HURLBERT, S. H. 1984. Pseudoreplication and the
design of ecological field experiments. Ecol.
Monogr. 54: 187-211.
JAMIESON, I., N. R. SEYMOUR, & P. R. BANCROFT. 1982.
Use of two habitats related to change in prey
availability in a population of Ospreys in north-
eastern Nova Scotia. Wilson Bull. 94: 557-564.
JENKINSß J.M. 1979. Foraging behavior of male and
female Nuttall Woodpeckers. Auk 96: 418-420.
KISIEL, D.S. 1972. Foraging behavior of Dendrocopus
villosus and D. pubescens in eastern New York State.
Condor 74: 393-398.
LEVINS, R. 1968. Evolution in a changing environ-
ment. Princeton, New Jerseyß Princeton Univ.
Press.
LIGON, J. D. 1968. Sexual differences in foraging
behavior in two species of Dendrocopus wood-
peckers. Auk 85: 203-215.
1973. Foraging behavior of the White-head-
ed Woodpecker in Idaho. Auk 90: 862-869.
MACARTHUR, R. H., & E.O. WILSON 1967. The theory
of island biogeography. Princetonß New Jerseyß
Princeton Univ. Press.
MCELLIN, S. M. 1979. Population demographies,
spacing, and foraging behaviors of White-breast-
ed and Pygmy nuthatches in ponderosa pine hab-
itat. Pp. 301-329 in The role of insectivorous birds
in forest ecosystems (J. G. Dickson et al., Eds.).
New York, Academic Press.
MORRISON, M.L. 1984. Influence of sample size and
sampling design on analysis of avian foraging
behavior. Condor 86: 146-150.
ß & K. A. WITH. 1987. Interseasonal and in-
tersexual resource partitioning in Hairy and
White-headed woodpeckers. Auk 104: 225-233.
MORSE, D.H. 1968. A quantitative study of foraging
of male and female spruce-woods warblers. Ecol-
ogy 49: 779-784.
PETIT, D. R., K. E. PETIT, & L. J. PETIT. 1990. Geo-
graphic variation in foraging ecology of North
American insectivorous birds. In Food exploita-
tion by terrestrial birds (M. L. Morrison et al.,
Eds.). Stud. Avian Biol. In press.
PETIT, L.J. 1989. Breeding biology of Prothonotary
Warblers in riverine habitat in Tennessee. Wilson
Bull. 101: 51-61.
., W. J. FLEMING, K. E. PETIT, & D. R. PETIT. 1987.
Nest-box use by Prothonotary Warblers (Protono-
taria citrea) in riverine habitat. Wilson Bull. 99:
485-488.
--, D. R. PETIT, K. E. PETIT, & W. J. FLEMING. 1990.
Annual variation in foraging ecology of Pro-
thonotary Warblers during the breeding season.
Auk 107: 146-152.
REYNOLDS, R. T., & E. C. MESLOW. 1984. Partitioning
of food and niche characteristics of coexisting
Accipiter during breeding. Auk 101: 761-799.
RICKLEFS, R. E., & M. LAU. 1980. Bias and dispersion
of overlap indices: results of Monte Carlo sim-
ulations. Ecology 61: 1019-1024.
ROBBINS, J. D. 1971. Differential niche utilization in
a grassland sparrow. Ecology 52: 1065-1070.
ROBINSON, S. K. 1986. Three-speed foraging during
the breeding season of Yellow-rumped Caciqus
(Icterinae: Cacicus cela). Ecology 67: 394-405.
ß & R. T. HOLMES. 1984. Effects of plant species
and foliage structure on the foraging behavior of
forest birds. Auk 101: 672-684.
ROOTß R. B. 1967. The niche exploitation pattern of
the Blue-gray Gnatcatcher. Ecol. Monogr. 37: 317-
350.
$CHOENER, T.W. 1968. The Anolis lizards of Bimini:
resource partitioning in a complex fauna. Ecol-
ogy 49: 704-726.
1971. Theory of feeding strategies. Annu.
Rev. Ecol. Syst. 2: 369-404.
1974. The compression hypothesis and tem-
poral resource partitioning. Proc. Natl. Acad. Sci.
71: 4169-4172.
SELANDER, R. K. 1966. Sexual dimorphism and dif-
ferential niche utilization in birds. Condor 68:
113-151.
SHERRY, T. W. 1979. Competitive interactions and
adaptive strategies of American Redstarts and
Least Flycatchers in a northern hardwoods forest.
Auk 96: 265-283.
SIEGELß S. 1956. Nonparametric statistics for the be-
havioral sciences. New Yorkß McGraw-Hill.
WAGNERß J.L. 1981. Visibility and bias in avian for-
aging data. Condor 83: 263-264.
WALLACEß R. A. 1974. Ecological and social impli-
cations of sexual dimorphism in five melanerpine
woodpeckers. Condor 76: 238-248.
WALSBERG, G. E. 1983. Ecological energetics: what
are the questions? Pp. 135-158 in Perspectives in
ornithology (A. H. Brush and G. A. Clarkß Eds.).
Londonß Cambridge Univ. Press.
WHITMORE, R.C. 1979. Short-term changes in vege-
tation structure and its effect on Grasshopper
Sparrows in West Virginia. Auk 96: 621-625.
WIENS, J. A. 1983. Avian community ecology: an
iconoclastic view. Pp. 355-403 in Perspectives in
ornithology (A. H. Brush and G. A. Clark, Eds.).
London, Cambridge Univ. Press.
-, S. G. MARTIN, W. R. HOLTHAUS, & F. A. IWEN.
1970. Metronome timing in behavioral ecology
studies. Ecology 51: 350-352.
WILLIAMS, J. B. 1975. Habitat utilization by four
species of woodpeckers in a central Illinois wood-
land. Am. Midi. Nat. 93: 354-367.
1980. Intersexual niche partitioning in
Downy Woodpeckers. Wilson Bull. 92: 439-451.
WILLIAMSON, P. 1971. Feeding ecology of the Red-
eyed Vireo (Vireo olivaceous) and associated fo-
liage-gleaning birds. Ecol. Monogr. 41: 129-152.
WINKLER, H. 1979. Foraging ecology of Strickland's
Woodpecker in Arizona. Wilson Bull. 91: 244-
254.
ZAR, J. H. 1974. Biostatistical analysis. Englewood
Cliffsß New Jersey, Prentice-Hallß Inc.