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2014 Southeastern Naturalist Notes Vol. 13, No. 1
A.J.J. Lehmicke and C.D. Jones
First Confirmed Records of Parasitism of Seaside Sparr ow Nests
by Brown-headed Cowbirds
Anna Joy J. Lehmicke1,* and Clark D. Jones1
Abstract - Molothrus ater (Brown-headed Cowbird) is a known nest parasite for numerous North
American passerines and has exacerbated the decline of many imperiled landbird species. However,
Brown-headed Cowbird habitat preferences do not frequently overlap with many salt marsh-dwelling
species. During intensive demographic research of Ammodramus maritimus (Seaside Sparrow) in
the coastal salt marshes of Mississippi (2010–2012), we documented the first instances of confirmed
nest parasitism of Seaside Sparrows by Brown-headed Cowbirds. We suggest that sea-level rise could
increase instances of nest parasitism in marsh-dwelling passerines by increasing the perimeter-to-area
ratio of marsh habitat and moving existing marsh in closer proximity to habitats preferred by Brownheaded
Cowbirds.
Ammodramus maritimus Wilson (Seaside Sparrow) is an obligate coastal marsh-dwelling
passerine that occurs in scattered populations from southern Maine to the northwestern
coast of the Gulf of Mexico in Texas (Post and Greenlaw 2009). Seaside Sparrows spend
their entire life cycle in coastal marshes, both breeding and wintering in the marsh. Little
is known about species-level population trends due to a lack of long-term and widespread
data, but a naturally limited total population due to restricted range (estimated at slightly
more than 100,000 individuals; National Audubon Society 2007) and threats to coastal wetland
habitat raise concerns for their future conservation status. They are on the Audubon
WatchList of species in need of conservation action due to their highly specialized habitat
needs and continuing habitat loss (National Audubon Society 2007). In addition, Seaside
Sparrows are categorized as a species of conservation concern throughout their range by the
US Fish and Wildlife Service (USFWS 2008) and are considered a Tier I species by the US
Partners in Flight (Rosenberg 2004).
Molothrus ater Boddaert (Brown-headed Cowbird) is an obligate brood parasite found
throughout the contiguous United States. While the species was initially restricted to
short-grass plains, human modification of habitat has allowed for significant range expansion
(Lowther 1993). Habitat fragmentation has also brought Brown-headed Cowbirds
into contact with many bird species previously protected from parasitism, particularly interior
forest species. Brown-headed Cowbird parasitism has been implicated in the decline
of many species, including the federally endangered Setophaga kirtlandii Baird (Kirtland’s
Warbler; Mayfield 1961) and Vireo atricapilla Woodhouse (Black-capped Vireo;
USFWS 1991).
While Brown-headed Cowbirds are found throughout the United States, they are not
found in all habitat types. Brown-headed Cowbirds are typically found in habitats with a
high perimeter-to-area ratio rather than open areas (Jensen and Cully 2005) or forest interior
(>350 m from the forest edge; Howell et al. 2007). Studies in recent years have found low
to no brood parasitism of coastal marsh-nesting passerines (Greenberg et al. 2006, Reinert
2006), suggesting this habitat is not preferred by Brown-headed Cowbirds, perhaps due to
absence of suitable perch sites. Here we document the first instances of widespread nest
1Warnell School of Forestry and Natural Resources, University of Georgia, Athens, GA 30602.
*Corresponding author - lehmicke@uga.edu.
Manuscript Editor: Roger W. Perry
Notes of the Southeastern Naturalist, Issue 13/1, 2014
2014 Southeastern Naturalist Notes Vol. 13, No. 1
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A.J.J. Lehmicke and C.D. Jones
parasitism of Seaside Sparrows by Brown-headed Cowbirds and suggest that increasing sea
levels may lead to higher levels of nest parasitism of tidal marsh-nesting passerine species.
Field-Site Description. We conducted fieldwork in two marshes in Jackson County, MS,
on the Mississippi Gulf Coast. Grand Bay National Estuarine Research Reserve (GBNERR;
30º19'N, 88º27'W) is composed of approximately 7400 ha of wetlands, pine savannas, and
terrestrial habitats. The tidal marsh areas are predominately polyhaline (salinity = 18−35
ppt; Cowardin et al. 1979) and are dominated by Juncus roemerianus Scheele (Needlegrass
Rush), interspersed with narrow bands of Spartina alterniflora Loisel (Atlantic Cordgrass).
The Pascagoula River Marsh Coastal Preserve (30º23'N, 88º34'W) is a 4600-ha site of
mostly oligohaline and mesohaline (0.5−5 ppt and 5−18 ppt; Cowardin et al. 1979) marsh,
dominated by J. roemerianus, S. alterniflora, and Spartina cynosuroides L. (Big Cordgrass).
Methods. During three breeding seasons (2010–2012), we conducted intensive demographic
work on seven plots (three at GBNERR, four on the Pascagoula River), averaging
about 4 ha each. Our primary research focus required finding and monitoring Seaside
Sparrow nests. We found nests during all nesting stages (building, laying, incubating, and
nestling) and checked them every two to four days until the nest failed or nestlings fledged.
We carefully noted nest contents during each check, although we attempted to minimize the
time spent at the nest in order to cause as little disturbance as possible.
Results. During three seasons of intense demographic work (2010−2012), we found five
Seaside Sparrow nests containing one Brown-headed Cowbird nestling each: four at the
Grand Bay National Estuarine Research Reserve and one in the Pascagoula River Marsh
Coastal Preserve. Of the five parasitized nests, one had only a Brown-headed Cowbird; at
least one Seaside Sparrow nestling was present in the remaining four (Fig. 1). The nestlings
in three of the five nests fledged, although we only observed an adult Seaside Sparrow feeding
a Brown-headed Cowbird fledgling from one of the three. Seaside Sparrow fledglings
are difficult to relocate and it was not unusual for us to never observe adults with fledglings,
even when we were confident that the nestlings fledged. Therefore, we are hesitant
to speculate on potential survival of Brown-headed Cowbird fledglings or Seaside Sparrow
fledglings from parasitized nests.
As part of our Seaside Sparrow demographic work, we monitored seven plots, but all
five of the parasitized nests were found on two of those plots. One of the two plots had
a high concentration of tall (>2 m) shrubs, providing ample perch sites for adult Brownheaded
Cowbirds. The second site had no shrubs, was comprised primarily of low-growing
S. alterniflora and Distichlis spicata L. (Inland Saltgrass), and was far from upland habitat
(≈3 km); however, on multiple occasions we observed both male and female adult Brownheaded
Cowbirds perched on PVC pipes used as survey markers.
It is likely that more than five nests were parasitized during the three summers. Brownheaded
Cowbird and Seaside Sparrow eggs are nearly indistinguishable without close
inspection (i.e., they are easily overlooked when trying to minimize disturbance to wellconcealed
nests), so a cowbird egg may have gone unnoticed in nests that failed before
hatching. Indeed, two of the five parasitized nests were found during incubation and the
presence of a cowbird was not recognized until the eggs hatched. At the two sites where
Brown-headed Cowbird nestlings were observed, we found 158 Seaside Sparrow nests over
the three breeding seasons. If we extrapolate from the proportion of hatched nests containing
a Brown-headed Cowbird nestling (5/84 or 5.95%), then potentially four out of the 74
nests that did not hatch at those sites contained a Brown-headed Cowbird egg. We do not
believe that we missed any Brown-headed Cowbird nestlings that were present, because
while Brown-headed Cowbirds and Seaside Sparrows are similar in size and mass on hatch
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2014 Southeastern Naturalist Notes Vol. 13, No. 1
A.J.J. Lehmicke and C.D. Jones
day and one day after hatching (cowbirds: 2.6 and 4.6 g [Scott 1979], sparrows: 2.4 and 3.8
g [Post and Greenlaw 2009]), Brown-headed Cowbirds can be distinguished upon hatching
as they are covered with white/light gray down compared to the Seaside Sparrows’ dark
gray down (Fig. 1).
Discussion. These observations are significant because they are the first records of
a Seaside Sparrow population with widespread parasitism by Brown-headed Cowbirds
and the first indisputable records of Seaside Sparrows successfully rearing and fledging
cowbirds. To our knowledge, the only previously published observation of a Seaside
Sparrow and Brown-headed Cowbird interaction involved adult Seaside Sparrows feeding a
fledgling Brown-headed Cowbird (Bagg and Eliot 1937). That account is generally accepted
as evidence that Seaside Sparrows can successfully raise Brown-headed Cowbirds, and the
sparrows are listed as hosts based on this observation (Friedmann 1963). However, Klein
and Rosenberg (1986) pointed out that classifying any species as a Brown-headed Cowbird
host based solely on the observation of an adult of the host species feeding a Brown-headed
Figure 1. Seaside Sparrow Ammodramus maritimus nestling (left) and Brown-headed Cowbird
Molothrus ater nestling (right), four days post-hatch.
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A.J.J. Lehmicke and C.D. Jones
Cowbird fledgling is problematic. There are numerous accounts of multiple species of adult
birds feeding the same fledgling Brown-headed Cowbird, clearly showing that fledgling
Brown-headed Cowbirds are sometimes fed by non-host adults (Klein and Rosenberg 1986,
Scott 1988). Additionally, Post and Greenlaw (2009) agree that this single observation in
itself is not proof that the same Seaside Sparrows incubated and fledged the Brown-headed
Cowbird, as Seaside Sparrows have been observed feeding both Agelaius phoeniceus L.
(Red-winged Blackbird; Rakestraw and Baker 1981) and Ammodramus caudacutus Gmelin
(Saltmarsh Sparrow; Post and Greenlaw 2009) fledglings.
A second, unpublished observation involved a likely Brown-headed Cowbird egg in
a probable Seaside Sparrow nest in Connecticut (C. Elphick, University of Connecticut,
Storrs, CT, pers. comm.). While the female was never observed well enough to definitively
say that it was a Seaside Sparrow nest, the nest structure and the general impression of the
flushing female suggest that it was a Seaside Sparrow rather than a Saltmarsh Sparrow. The
egg was noticeably larger and the spotting pattern and background coloration were distinct.
Notably, this egg was the only evidence of cowbird parasitism out of over 1100 Saltmarsh
Sparrow nests and 100 Seaside Sparrow nests observed during the study, suggesting that
there may be differences in susceptibility to parasitism among populations. Even with these
two records, our observations still provide the first undeniable evidence that Seaside Sparrows
can successfully incubate, raise, and fledge Brown-headed Cowbirds and that there are
populations where such parasitism is a regular occurrence.
While Brown-headed Cowbirds do not seem to be a current threat to Seaside Sparrow
populations, there is real potential this could change in the near future. Brown-headed Cowbirds
are edge specialists and rising sea levels will likely push salt marshes farther inland
or force Seaside Sparrows to nest closer to the upland edge of marshes. These changes will
potentially increase the risk of cowbird parasitism of Seaside Sparrow nests, especially
since Seaside Sparrows are “good” hosts, meaning that they can successfully fledge cowbird
young. Additionally, if Seaside Sparrow habitat retreats farther inland, other predation pressures
will likely increase. In fact, surveys conducted over three breeding seasons indicate
that abundance of Seaside Sparrows in our study area is lower at sites with a higher proportion
of upland habitat, possibly due to proximity of predator source populations (A.J.J.
Lehmicke, unpubl. data). These increased predation pressures will likely be exacerbated
by brood parasitism. Recognizing Brown-headed Cowbirds as a potential threat to marshnesting
passerines, at least along the northern coast of the Gulf of Mexico, can allow for
monitoring and management before they become a population-level problem.
Acknowledgments. Our fieldwork was supported by grants from the Georgia Ornithological
Society and the United States Fish and Wildlife Service through the Gulf Coast Joint
Venture. We thank M. Woodrey and R. Cooper for guidance on this project, and our field
assistants L. Duval, J. Jetchev, K. Morris, A. Densborn, and C. Randall.
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