Both sexes build a large sodden, floating nest of rotting and green plant material and mud. The decomposition of plant material generates substantial quantities of heat, up to 11-13C higher than the surrounding water, providing enough heat to incubate the eggs in the adults' absence (Davis et al. 1984). Like other grebe species (Nuechterlein and Buitron 2002) this may afford the adults the ability to roost comunally at night to minimize predation risk.
The pied-billed grebe was recorded as a probable or confirmed breeder in 150 USGS topographical quads during the second New York State Breeding Bird Atlas (2000-2005), and as a possible breeder in an additional 115 quads. Overall, the species is considered a rare to uncommon, local breeding species with many of the records clustered in areas of large wetland complexes. Although it was recorded in significantly more quads during the Atlas 2000 project in comparison with the first New York State Breeding Bird Atlas in the mid-1980's, Breeding Bird Survey records indicate a - 2.0% annual trend between 1980 and 2002 (New York State Department of Environmental Conservation 2006) and the species is state listed as Threatened. Loss of wetlands and other factors continue to pose threats to the species although a number of excellent occurrences are on protected state and federal wetland complexes.
Although Breeding Bird Survey data for 12 survey routes in New York between 1966-1989 showed a non-significant 0.6% decrease in abundance (Gibbs and Melvin 1992) another analysis shows a - 2.0 % annual trend from 1980-2002 (New York State Department of Environmental Conservation 2006). An increase in the number of Breeding Bird Atlas blocks where the species was either a probable or confirmed breeder from the first Atlas to the second (86 to 184) Atlas could reflect population increases, range expansion, or increased surveys efforts for marshbird species.
There is little data on which to base a long-term trend. However, considering the massive loss of wetlands in New York State over the past 100 years, it seems that pre-European population sizes must have been substantially higher. Heavy historical exploitation by humans, namely shooting for feathers and egg collecting, have abated since the turn of the 20th century. In the late 1800's large numbers were shot and sold to milliners and furriers who fashioned ear-muffs and hat ornaments from the silver-white breast and abdomen feathers (Bent 1919).
Currently, the greatest threat to this species is the ongoing alteration and loss of wetlands through draining, dredging, filling, pollution, invasive species and siltation from agricultural practices and roads. These threats lead to the degradation, isolation, and fragmentation of wetlands and have left many marshes that were too small, or were not part of larger marsh complexes, unsuitable for grebes and other marshbirds (New York State Department of Environmental Conservation 2006). Pollution and environmental contamination degrades the food web of wetland ecosystems and can impair the reproductive capacity of pied-billed grebes through the process of biomagnification. Popular organophosphate pesticides used heavily for agriculture have been directly implicated in the death of this species and elevated mercury levels have been detected in some individuals (Gibbs and Melvin 1992). Siltation and runoff from development and agriculture may also negatively impact populations of important prey species. Water level management on Lake Ontario and other large water bodies can alter marsh habitat and decrease the quality of historically utilized sites. In other cases, lack of stochastic events that produce a flushing effect may negatively impact marshbirds by promoting large monotypic stands of emergent vegetation. Invasive aquatic plants such as purple loosestrife crowd out native emergents and form stands too dense, and lacking sufficient open water interspersion, for some marshbird species including pied-billed grebes. Small, localized breeding populations are extremely vulnerable to stochastic events, such as storms, habitat loss, or human disturbance. (New York State Department of Environmental Conservation 2006). Grebes are sometimes mistaken for ducks by hunters and are accidentally shot. Television and cell towers pose an extreme danger to nocturnally migrating individuals, for example 65 pied-billed grebes died at a television tower in Florida between 1955 to 1980 (Muller and Storer 1999).
Restoration of wetland habitat, improvement of water level control at managed wetlands, promotion of the Farm Bill Landowner Incentive Program to manage and restore appropriate habitat, reducing the spread of invasive exotic species, and controlling invasive species where they occur at sites occupied by grebes and other rare marshbirds, are all identified as important management actions beneficial to pied-billed grebes (New York State Department of Environmental Conservation 2006). Because pied-billed grebes will readily colonize wetland impoundments managed primarily for waterfowl, there is ample opportunity to make minor alterations to existing management schemes to improve nesting and foraging habitat for grebes. Since other secretive, rare marshbird species such as American bitterns, least bitterns, and black terns share habitat preferences with pied-billed grebes, management strategies could benefit multiple species of management concern. The conservation of relatively large (5-75 ha) wetlands with roughly a 50/50 interspersion of moderately shallow emergent vegetation and open water (the "hemi-marsh") is the most urgent management need for pied-billed grebes and other marsh-nesting birds. Dense stands of vegetation therefore need to be periodically opened up to retard succession. Properly managed muskrat populations often fulfill this role, but the process may need to be augmented by cutting, burning or flooding. Herbicide treatments are not recommended. Manipulation of water levels provides a cost-effective method for establishing moderately dense stands of emergent vegetation while retaining open water areas preferred by grebes. However, water levels need to be maintained at a stable level during the nesting season to prevent flooding of nests and predator access. Complete drawdown should be avoided so as not to destroy major fish and odonate food items. The floating nests of grebes are easily washed over and capsized by wave action, so large motorized boats should be excluded from occupied marshes, and nesting areas should be protected from heavy recreational use to prevent disturbance of incubating birds (Gibbs and Melvin 1992). In general, pied-billed grebe's high reproductive potential (large clutch size, ability to re-nest following nest loss), in addition to its tolerance of a wide range of freshwater marsh habitats, suggests that management potential is high.
A number of research needs have been identified including: 1) Evaluation of habitat characteristics at multiple scales to better understand micro and macro habitat features important for nest site selection; 2) Conducting controlled experiments to see which management actions are effective locally in producing suitable habitat; 3) Conduct demographic studies at selected sites to identify source and sink populations; 4) Determine major migration stop-over sites and conduct studies of habitat use, prey availability, and diet at migratory staging and molting areas, as well as wintering grounds, to asses possible threats and limiting factors, 5) Investigate aspects of behavioral ecology, such as mate selection, mate fidelity, spacing behavior, coloniality, dispersal, and post fledging parental care; 6) Periodically monitor the levels of contaminants in birds and eggs to assess trends and determine effects on eggshell thinning, behavioral modification, chick development, nesting success, and juvenile survival; 7) Refinement of standardized survey techniques and implementation of programs to monitor population trends; 8) Conduct studies of the structural composition of wetland vegetation, water levels and quality, and wetland area and occupancy relationships during nesting and migration; 9) Evaluate the effects of invasion of non-native invasive marsh plants on grebe habitat suitability (Gibbs and Melvin 1992, New York State Department of Environmental Conservation 2006) .
Pied-billed grebes inhabit quiet marshes, marshy shorelines of ponds, shallow lakes, or marshy bays and slow moving streams with sedgy banks or adjacent marshes; rarely in brackish marshes with limited tidal fluctuation. Although plant species in breeding marshes may vary, a 50/50 combination ("hemi- marsh") of emergent vegetation interspersed with open water is desirable (Andrle and Carroll 1988). Grebes avoid dense emergent vegetation, and muskrats appear to play an important role in opening up dense cattail stands and providing cut stalks for nest construction. Ideal water depths for nesting range from 25 to 50 cm (Seyler 2003). Grebes set up breeding territories more commonly in wetlands impounded by beavers or humans than in those of glacial origin, and individual pairs appear to favor wetlands of intermediate size (0.6 - 7.0 ha) over very large or small wetlands (Gibbs and Melvin 1992).
As a breeding species, the pied-billed grebe occurs statewide, with concentrations on the Lake Ontario Plain and St. Lawrence Valley. It is more sparsely distributed in the Adirondacks, Catskills, Allegheny uplands, and on Long Island. It is a rare but regular winter visitor, more common on the coast, but also lingering fairly regularly in open water areas on the Allegany and Oswego Rivers, and at Dunkirk Harbor in Chautauqua County (Levine 1998).
BREEDING: southeastern Alaska through southern Canada to Nova Scotia, south locally through North America, Middle America, West Indies, and South America to central Chile and southern Argentina (AOU 1983). Breeding populations in the northeastern U.S. are more localized and less abundant than in other regions of the U.S. or Canada (Gibbs and Melvin 1992). NON-BREEDING: southern British Columbia, western and southern U.S. south through South America. Areas of high winter concentrations include southern and central Texas, Great Salt Lake (Utah), Lake Mead (Nevada-Arizona), and the San Joaquin Valley (California) (Root 1988). The highest overall counts of wintering grebes occurs on the Tennesse River in northeastern Alabama (Gibbs and Melvin 1992).
Pied-billed grebes are small, stocky, poorly buoyant waterbirds, about 31-38 cm in length, with small, narrow wings, and feet placed far back, with a blunt-ended posterior. During the non-breeding period, the bill is unmarked, the throat is white, and the white rear becomes more conspicuous. As adults, the sexes are alike, whereas juveniles are distinguished by the lack of a white orbital ring, an unmarked bill, darker brown sides of the head and neck, and a whiter underbelly (Palmer 1962). Downy chicks have a zebra-like pattern of black and white stripes, interspersed with reddish-brown spots (Palmer 1962). VOCALIZATIONS: Territorial males have a distinctive prolonged call, a loud "cow-cow-cow-cow-cow- cowp...cowp...cowp...". Several other calls are also produced during the breeding season, but during the non-breeding season they are mostly silent. NEST: Grebes build sodden, floating nests of rotting and green plant material and mud averaging 38 cm in diameter (Glover 1953), often anchored to growing emergent plants. EGGS: Elliptical to subelliptical, approximately 44 x 30 mm, smooth and nonglossy (Harrison 1978). Although white or tinted bluish when laid, the eggs gather a heavy, brown stain from the wet, organic matter in the nest.
Mature adults are easiest to identify and the sexes are similar. However, the downy chicks of pied-billed grebes have a striking, zebra-like pattern of black and white stripes, interspersed with reddish-brown spots, that makes them readily identifiable as well.
Grebe's are very secretive birds that will slowly submerge underwater with only their eyes and nostrils showing in order to escape danger. Downy chicks ride on the adults back, even when they dive underwater. Adults consume their own feathers and also feed them to young, presumably to protect the stomach and trap fish bones. Hard indigestible items are felted together with feathers and regurgitated as pellets. Grebes migrate nocturnally, landing before dawn at the nearest waterbody and are more social outside the breeding season. During breeding pied-billed grebes are an aggressive, highly territorial bird, threatening, chasing and attacking conspecifics and other species. They are reluctant to take flight, needing a long running start across open water to become airborne. Seasonally monagamous, both sexes build the nest and add plant material and mud as the season progresses and the nest slowly sinks. Air-pockets and trapped gases generated by the fermenting and rotting vegetation give buoyancy to the nest. The floating, rotting nest generates substantial quantities of heat (Davis et al. 1985) and may allow the adults to abandon the nest at night to avoid predation risk (Nuechterlein and Buitron 2002). The young are precocial, making their first successful catches of food (fish, insects) at 10-12 days post-hatching and they are capable of flight only 35 days after hatching.
Pied- billed grebes are opportunistic carnivores, the diet being dominated by crayfish (31% by volume), insects (46%), primarily Odonates (dragonflies), Heteroptera (true bugs), Coleoptera (beetles) and fish (24%), including catfish, eels, perch, sunfish, suckers, carp, sciulpins, killifish, sticklebacks, and minnows. There is a strong seasonal shift in the diet, fish being most important during the nonbreeding season, while dragonfly nymphs constituted 34% of the diet in late summer and are an important food item for chicks (Muller and Storer 1999). The diet also includes smaller amounts of snails, small frogs, tadpoles, aquatic worms and leeches. In wetlands where fish are not prevalent, Ambystomatid salamander adults and larvae play a key role in the diet (Osnas 2003).
In New York, the pied-billed grebe is a rare to uncommon local breeder; a fairly common migrant, more numerous in the fall; and a rare but regular winter visitant (Levine 1998). Migratory grebes usually arrive on the nesting grounds by early March, shortly after ice out, and courtship commences in early April with nesting activity initiated by mid-April. The peak vocalization period for pied-billed grebes at study sites in western New York was from late-April through mid-May with breeding activity vocalizations dropping off through June (Lor and Maleki 2002).
The time of year you would expect to find Pied-billed Grebe active and reproducing in New York.
Podilymbus podiceps (Linnaeus, 1758)
Grebes are a family of diving birds with no living relatives. They may have once been related to Loons (Cotter and Spencer 1996).
American Ornithologists' Union (AOU). 1983. Check-list of North American Birds, 6th edition. Allen Press, Inc., Lawrence, Kansas. 877 pp.
Andrle, Robert F. and Janet R. Carroll, editors. 1988. The atlas of breeding birds in New York State. Cornell University Press. 551 pp.
Bent, A.C. 1919. Life histories of North American diving birds. U.S. Natl. Mus. Bull. 107. Washington, D.C.
Bull, John. 1964. Birds of the New York area. New York: Harper and Row Publications 540 pp.
Bull, John. 1974. Birds of New York State. Doubleday, Garden City, New York. 655 pp.
Chabreck, R. H. 1963. Breeding habits of the pied-billed grebe in an impounded coastal marsh in Louisiana. Auk 80:447-52.
Cotter, R.C., and M. Spencer. 1996. Podilymbus podiceps. Pages 210-213 in J. Gauthier and Y. Aubry, editors. The breeding birds of Quebec. Canadian Wildlife Service, Environment Canada, Montreal.
Davis, T.A., M.F. Platter-Reiger, and R.A. Ackerman. 1985. Incubation water loss by pied-billed grebe eggs: Adaptation to a hot, wet nest. Physiological Zoology 57:384-391.
Gibbs, J. P., and S. M. Melvin. 1992. Pied-billed grebe, PODILYMBUS PODICEPS. Pages 31-49 in K. J. Schneider and D. M. Pence, editors. Migratory nongame birds of management concern in the Northeast. U.S. Fish and Wildlife Service, Newton Corner, Massachusetts. 400 pp.
Glover, F. A. 1953. Nesting ecology of the pied-billed grebe in northwestern Iowa. Wilson Bulletin 65:32-9.
Harrison, C. 1978. A Field Guide to the Nests, Eggs and Nestlings of North American Birds. Collins, Cleveland, Ohio.
Herkert, J. R., editor. 1992. Endangered and threatened species of Illinois: status and distribution. Vol. 2: Animals. Illinois Endangered Species Protection Board. iv + 142 pp.
Johnsgard, P. A. 1987. Diving birds of North America. Univ. Nebraska Press, Lincoln. xii + 292 pp.
Levine, E. 1998. Bull's birds of New York State. Comstock Publishing Associates, Ithaca, NY.
Lor, S. and R.A. Malecki. 2002. Call- response surveys to monitor marsh bird trends. Wildlife Society Bulletin 30:1195-1201.
Morgan, A.H., R.A. Forster, and W.R. Meservy. 2003. Pied-billed grebe, Podilymbus podiceps. Pages 26-27 in W.R. Petersen and W. R. Meservy, editors. Masssachusetts Breeding Bird Atlas. University of Massachusetts Press, Boston.
Muller, M.J., and R.W. Storer. 1999. Pied-billed Grebe (Podilymbus podiceps). No. 410 in The Birds of North America, A. Poole and F. Gill, editors. The Birds of North America, Inc., Phildelphia.
Neuchterlein, G.L., and D. Buitron. 2002. Nocturnal egg neglect and prolonged incubation in the Red-necked grebe. Waterbirds 25:485-491.
New York Natural Heritage Program. 2006. Biotics Database. Albany, NY.
New York Natural Heritage Program. 2019. New York Natural Heritage Program Databases. Albany, NY.
New York State Department of Environmental Conservation, Division of Fish, Wildlife, and Marine Resources. 2006. New York State Comprehensive Wildlife Conservation Strategy. Albany, NY: New York State Department of Environmental Conservation.
Osnas, E.E. 2003. The role of competition and local habitat conditions for determining occupancy patterns in grebes. Waterbirds 26:209-216.
Palmer, R. S. (editor). 1962. Handbook of North American birds. Vol. 1. Loons through flamingos. Yale University Press, New Haven. 567 pp.
Root, T. 1988. Atlas of wintering North American birds: An analysis of Christmas Bird Count data. University of Chicago Press. 336 pp.
Seyler, D.A. 2003. Pied-billed grebe (Podilymbus podiceps) densities in a western New York impoundment. The Kingbird 53:195-202.
Terres, J. K. 1980. The Audubon Society encyclopedia of North American birds. Alfred A. Knopf, New York.
U.S. Fish and Wildlife Service (USFWS). 1995. Migratory nongame birds of management concern in the United States: The 1995 list. Office of Migratory Bird Management, U.S. Fish and Wildlife Service, Washington, DC. 22 pp.
Information for this guide was last updated on: May 1, 2019
Please cite this page as:
New York Natural Heritage Program. 2019. Online Conservation Guide for Podilymbus podiceps. Available from: https://guides.nynhp.org/pied-billed-grebe/. Accessed May 20, 2019.