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Introduction

Coastal Marine Habitats

Estuarine Ecosystems

Wetland Ecosystems

Riverine Ecosystems

Old Fields

Pine Forests

Conservation Issues

References

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Birds

Introduction

Barn swallowAll birds share the following characteristics: (1) tetrapods with feathers; (2) forelimbs modified to form wings; (3) respiration through lungs; (4) endothermic; (5) internal fertilization; (6) shelled amniotic eggs; and (7) acute vision (Campbell 1993). Birds fill a wide range of ecological roles. Nectar-eating species such as hummingbirds, herbivorous species such as ducks which feed on aquatic vegetation, and granivorous species such as doves and buntings all depend on plant matter for a substantial portion of their diet. These species represent primary consumers in the food web. Insectivorous species such as swallows and warblers, and shorebird species such as plovers and sandpipers that feed on crustaceans and molluscs represent the next higher trophic level. Omnivorous species such as grackles and crows eat a combination of plant and animal matter which represent multiple trophic levels. Raptor species such as hawks, eagles, and owls represent the highest bird trophic level. These birds feed on mammals, reptiles, and amphibians as well as other birds and are considered top predators. Scavengers such as vultures and gulls play an important role in removal of dead animal matter and nutrient recycling.

The ACE Basin study area has an extremely rich bird life. Over half of the species of birds that occur in North America inhabit the 320,000 hectares (790,000 acres) of the ACE Basin study area. Several bird surveys have been conducted in the ACE Basin study area. The South Carolina Department of Natural Resources (SCDNR) Wildlife and Freshwater Fisheries division has conducted colonial waterbird surveys since 1969. This program uses both ground and aerial surveys to determine the number of various birds species that nest in colonies in the ACE Basin study area. Nesting colonies can be found in a variety of habitats including upland forests, forested wetlands, beaches, and bird keys (Colonial waterbird nest locations {map icon}). The South Carolina Center for Birds of Prey{exit icon} has conducted the South Carolina Coastal Hawk Migration Survey since 1995. This survey focuses on the hawk species that migrate into coastal South Carolina during the winter. The ACE Basin survey site is located three miles inland on Edisto Island in estuarine marsh habitat surrounded by forested wetlands, croplands, and upland forests. The United States Geological Survey (USGS) has conducted the Breeding Bird Survey (BBS) {short description of image} in the ACE Basin study area at a site near Walterboro since 1970. This is a large-scale roadside survey of North American birds with the objective of estimating population change for songbirds. The Walterboro route of this survey travels through upland forests, forested wetlands, and old- field habitats (Breeding bird survey route {short description of image}). The Audubon Society has coordinated the Christmas Bird Count (CBC) {short description of image} in the ACE Basin study area since 1990. Groups of volunteers work together to identify and count all birds possible within a 24-km (15-mile) circle. The survey site is centered at Brickyard Launching Bridge, Bennetts Point Road and includes both freshwater and estuarine non-forested wetlands, forested wetlands, upland forests and old- field habitats (Christmas bird survey {short description of image}). The SCDNR has compiled an ACE Basin Bird Checklist that lists all the birds inhabiting the area along with their residency and abundance status.

There are about 8,600 species of birds in the world divided into 28 orders. Of these, approximately 280 species of birds in 17 orders occur in the ACE Basin study area. Many of these birds migrate in tremendous numbers to South Carolina from northern breeding grounds to spend their winters or to rest before continuing their migration to more southern areas. Because birds can fly, the barriers that restrict travel for many animals are easily avoided by birds. Therefore, birds are rarely restricted to one environment and are often found in a variety of habitats (Potter et al. 1980). However, birds frequently exhibit a preference of one habitat over others and this habitat preference affects distribution and abundance. The avifauna of different habitats in the ACE Basin study area will be discussed below. This discussion is based mainly on information obtained from Sandifer et al. (1980) and Potter et al. (1980).

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CormorantCoastal Marine Habitats

Marine Subtidal Waters
An estimated thirty species of birds utilize the marine subtidal habitat as feeding grounds. Eight of these species are common year-round residents and seven are common in winter (Bird habitat {short description of image}warning icon). Five species that utilize this habitat (e.g. shearwaters, phalarope, gannet, and petrel) are mainly pelagic and are seen only rarely near shore. The concentration of fish and invertebrates by the Gulf Stream provide ample prey for these birds. The majority of birds in this habitat are piscivorous and catch fish by aerially diving (e.g. terns, gannets); surface diving (e.g. loons, cormorants); or surface skimming (skimmers, gull-billed terns). Two species (e.g. Wilson’s petrel and northern phalarope) feed on nearshore zooplankton while diving ducks consume benthic organisms (Sandifer et al. 1980). The brown pelican and the double-crested cormorant are probably the most common permanent resident species that feed in subtidal habitats of the ACE Basin study area. Double-crested cormorants dive from the surface to feed on small fish and can often be seen swimming with just their head and neck above water. These birds feed in subtidal waters but are most likely to nest in stunted cypress trees along heavily forested lake shores (Potter et al. 1980).

Beaches
peregrine falconAn estimated forty-four avian species can be found on the intertidal beaches of the ACE Basin study area. Twenty-three of these are common year-round residents of the beaches. The avifauna community of beaches can be divided into three broad categories: (1) marine species such as brown pelicans, royal terns, and black skimmers which feed on fish and use the beaches only for resting or breeding; (2) macrobenthic predator species such as sanderlings, American oystercatchers, plovers, and sandpipers which hunt in the sand for annelids, crustaceans, and mollusks; and (3) beach scavengers such as gulls, crows, boat-tailed grackles, and vultures which feed mostly on dead animal matter that litters the beaches (Sandifer et al. 1980).

Although most species of birds found on beaches are not limited to this environment, there are a few species (e.g. sanderlings, red knots, piping plovers, and Wilson’s plover) which almost exclusively inhabit beaches. Sanderlings are small shorebirds that forage for mollusks, worms, and crustaceans in the surf zone. These birds are common year-round residents of the ACE Basin study area but breed in the Arctic (Sandifer et al. 1980). Brown pelicans are one of the most common marine seabirds seen on the beach. This species breeds on bird keys and feeds on fish by plunging from the air into the ocean. Both the black and turkey vulture can be seen on ACE Basin beaches. These birds hunt for carrion in a variety of habitats but nesting occurs most often in woodlands or swamps. Black vultures mostly hunt by sight over open habitat while turkey vultures are most often forest hunters and therefore depend on smell to locate prey. Both species are common year-round residents and are important ecologically because of their consumption of dead animal matter. The peregrine falcon is a winter predator in this habitat and is regularly seen in the ACE Basin study area during the fall migration in October. This species is endangered due to pesticide exposure, but numbers in the ACE Basin study area are steadily increasing as the bird recovers. Peregrine falcons are frequently seen perched low on remote barrier island beaches where they feed on shorebirds (Murphy, pers. comm.).

Bird Keys
Bird keys and banks are small isolated islands that usually occur in tidal inlets and broad bays. They are very dynamic habitats because they are susceptible to over wash by storm action and spring tides and because they tend to migrate in response to inlet morphology (Sandifer et al. 1980). Bird keys are used by a number of colonial birds for breeding because they provide protection from terrestrial predators such as raccoons. Historically, several bird keys in the ACE Basin study area were utilized by colonial waterbirds. However, recent anthropogenic alterations in channel flows have destroyed these keys (i.e. Egg Bank Island at the mouth of Harbor River). Currently, the only bird key in the ACE Basin study area on which birds nest is Deveaux Bank at the mouth of the North Edisto River.

Laughing gullTwelve species of birds are estimated to currently nest on Deveaux Bank. Forty-two percent of all colonial waterbird nests identified in the ACE Basin study area since 1969 were found to occur on Deveaux Bank (Colonial waterbird nesting sites {table icon}). Royal terns, brown pelicans, laughing gull, sandwich terns, and black skimmers are the dominant nesting species on bird keys (Colonial waterbirds. Colonial birds that breed on bird keys exhibit distinct habitat preferences. Brown pelicans prefer higher grounds where there is sufficient vegetation for nest construction. The number of brown pelican nests on Deveaux Bank has decreased since the 1970s (Pelican abundance {short description of image}) probably because of erosion of Deveaux Bank over the past 20 years. Prior to the 1970s, pelican populations declined because of DDT but since the ban on DDT in 1972, pelican populations have been on the rise and in 1985 they were delisted as an endangered species on the Atlantic coast. Royal tern nests are nothing more than depressions in the sand; if the nest is destroyed, a new nest is built and new eggs are laid. Royal tern colonies are the largest colonies on Deveaux Bank with thousands of nests often present during one breeding season (Royal tern abundance {short description of image}). Sandwich terns also occur in large numbers and nest in mixed colonies with royal terns. Laughing gulls establish their colonies on the fringes of brown pelican and royal tern colonies in order to exploit the food source provided by pelican and tern eggs and young. Since 1975, laughing gull nests have been recorded in the ACE Basin study area only at Deveaux Bank. Both black skimmers and gull billed terns nest in unvegetated areas of Deveaux Bank above the mean high tide mark.

Dunes
The maritime dune habitat is a harsh environment with many stressful physical attributes (e.g. blowing sand, high summer temperature, limited freshwater and sparse vegetation). Sea oats are the dominant plants and the abundance of seeds are food for the many granivorous birds which inhabit the dunes. Seeds make up the bulk of the diet for eleven of these species of birds including doves, blackbirds, sparrows, and cardinals. The Savannah sparrow is a common winter resident that feeds on dune plant matter. This species consumes more insects than other sparrows but the majority of the diet consists of grass and weed seeds. Insectivores (e.g. nighthawk, swallows, chimney swift, and warblers) are the next largest trophic group. The common nighthawk is a common summer resident which nests directly on the sand dunes and in many other open areas. These birds eat a variety of insects including flying ants, mosquitos, beetles, and gnats. The fish crow is the dominant scavenger and the great horned owl is the most abundant raptor. Large numbers of great horned owls have been observed hunting over sandy beaches for rodents and waterfowl (Sprunt and Chamberlain 1970).

Shorebirds such as terns, plovers, and sandpipers use the dunes for resting, feeding, and nesting. The least tern uses the dune habitat for breeding habitat with nesting occurring in the fore dune area. The least tern has declined in numbers over the years because of anthropogenic disturbance of beach habitats and is now listed as a state threatened species. This species has adapted to the changing environment by establishing nesting colonies on rooftops. Large shopping centers with gravel rooftops can support a surprising number of least tern nests. However, gravel rooftops have recently been replaced by rubber rooftops which are less expensive. Only K-mart still maintains the gravelled rooftops which can be used as nesting sites by the least tern (Murphy pers. comm.).

Maritime Shrub
Moving inland from the dune community, is the maritime shrub community which offers fewer habitats to bird species than does the nearby maritime forest. The lack of an understory and the low plant density provide little food for granivorous and herbivorous species. Many species in this habitat are omnivorous either year round (mockingbird and grackles) or seasonally (tree swallows). Most species in the shrub community consume insects (e.g. kingbird, yellow-throat, and sparrow hawk). The majority of species in this habitat are residents of the adjacent dune or maritime forests and utilize the shrub community only as feeding or nesting grounds. Two species, tree swallow and yellow-rumped warbler, are closely associated with this habitat because during cold weather when insects are scarce they consume wax myrtle berries. Also, the ground dove nests in wax myrtle and is, therefore, dependant on this habitat. Ground doves are granivores and consume a wide variety of seeds. This species is currently a state-threatened species along with the least tern, glossy ibis, and Wilson’s plover. A top predator in this habitat is the sharp-shinned hawk which is a fairly common winter resident. This raptor inhabits woodlands and ventures into the shrub community to hunt for small birds, insects, and small mammals.

Maritime Forests
painted bunting Maritime forests provide more diverse habitats than the beach, dunes, or shrub habitats, therefore, they contain a more diverse avian community. The dense vegetation and low canopy height of undisturbed maritime forests, however, act to decrease habitat types compared to inland forests. Therefore, avian species diversity is usually lower than that in inland forests (Sandifer et al 1980). Of the 280 birds found in the ACE Basin study area, almost one- third (87) can be found in the maritime forests . Many of the birds in the maritime forests are passerine birds including flycatchers, swallows, crows, nuthatches, wrens, kinglets, thrushes, vireos, warblers, sparrows, blackbirds, grackles, and finches. Insects make up all or part of the diet of most passerine birds with grains and fruits also important. Warblers, swallows, vireos, and flycatchers feed almost exclusively on insects, while sparrows, buntings, and finches feed mainly on vegetarian matter such as fruits, seeds, and grains (Sprunt and Chamberland 1970). The yellow-rumped warbler, or myrtle warbler, is the most common winter warbler in the ACE Basin study area. This species consumes many small insects along with the fruits of various plants (e.g. waxmyrtle and bayberry). The painted bunting is probably the most visually spectacular bird found in this habitat. This species is a common summer resident that builds its nest in bushes, trees, or Spanish moss and raises up to three broods a year. Turkey and black vultures are both common year-round scavengers in maritime forests. Top year-round predators in the maritime forests include three species of owls (screech owl, barred owl, and great horned owl) and two species of hawks (red-tailed and red-shouldered). The red-shouldered hawk occupies the ecotone between wetlands and forests and frequently feeds in wetland forests (Murphy pers. comm.). This species nests high in large trees near dense woodlands and feeds mostly on frogs and snakes.

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Estuarine Ecosystems

Lesser scaupThe estuarine subtidal habitat is an open water system used mainly by birds for resting and feeding. All of the birds found in this habitat are water birds which feed on fish, benthos, carrion, or insects. Three species of gulls (laughing, herring, and ring-billed) are considered common year-round residents of the ACE Basin study area. Herring and ring-billed gulls are abundant in winter but rare in other seasons and laughing gulls are abundant in summer but rare in winter. All three species eat a variety of food items and are important in the consumption of dead animal matter. Terns, cormorants, and brown pelicans inhabit open water areas to feed on fish. The double-crested cormorant is a common year-round resident that doesn’t breed in South Carolina. Other water birds such as the lesser scaup, ring-necked duck and ruddy duck feed on aquatic vegetation. The lesser scaup is a common winter resident that breeds in Canada. It eats the seeds of water lilies, pondweed, water milfoil, and widgeon grass along with mollusks, crustaceans, and insects. The osprey is the only bird of prey to utilize this habitat where it feeds on its primary prey, fish. Ospreys can be seen year-round but are rare in December and January.

The intertidal salt marshes provide habitat for a variety of avian species. Eighty-seven species of birds utilize salt marshes for feeding or breeding. Thirty-two of these are common year-round residents while an additional thirteen are common winter residents. Wading birds such as herons and egrets use this habitat for feeding on their primary prey which includes mummichogs, mullet, menhaden, and penaeid shrimp. Other birds such as rails, swallows, wrens, and blackbirds use the smooth cordgrass as feeding and nesting grounds. The clapper rail is a strict inhabitant of ACE Basin salt marshes. This species feeds, roosts, nests, and raises its young on the Spartina marsh (Sandifer et al. 1980). The clapper rail feeds on crabs, minnows, shrimp, and marsh insects and, in turn, is an important food item for a variety of mammalian and avian predators.

Northern harrierTwo sparrows, the sharp-tailed and the seaside, also rely heavily on salt marshes. The sharp- tailed sparrow is a common winter resident while the seaside is a year-round resident that nests on the marsh surface where Juncus and Spartina are the dominant plants (Bent 1968). Both species consume mostly animal matter including insects, crustaceans, and marine worms. The insectivorous long-billed marsh wren is another dominant species of the salt marsh. This species is found only in estuarine and freshwater wetlands and its eggs and young are heavily preyed upon by salt marsh mammals such as raccoons, marsh rice rats, and minks. Four raptors are found in estuarine emergent wetlands. Of these, the northern harrier or marsh hawk is probably the most important. This raptor is a common winter resident that is most abundant during migrations. Marsh hawks prey upon rodents and small birds that inhabit the marsh.

The abundance of fish and invertebrates in intertidal flats provides excellent feeding opportunities for many avian species. Fifty-five species of birds are estimated to occur in this habitat and over half of these are common year-round residents in the ACE Basin study area. Almost all of the species found here are wading birds or shorebirds including herons, egrets, ibises, gulls, plovers, sandpipers, and terns. The boat-tailed grackle and fish crow are the only non-aquatic species found regularly on intertidal flats. Both species feed on small fish and invertebrates.

Eight species of herons and egrets utilize the intertidal flats as feeding grounds with the great egret, snowy egret, and tricolored (Louisiana) heron being the most abundant. Many of the shorebirds feed extensively in this habitat but breed in others (e.g. beaches or bird keys). Migrations into and out of the intertidal flats can greatly affect abundances of some shorebirds in this habitat. Abundances of herring gulls, ring-billed ducks and American oystercatchers increase in the winter as northern birds migrate south. Other species such as the semipalmated plover, ruddy turnstone, and least sandpiper decline in abundance during the summer as they leave to breed in other habitats.

The American oystercatcher is possibly the most notable bird in this habitat. Although it breeds on beaches, this bird feeds exclusively on the flats. Oystercatchers feeds mainly on mollusks including oysters and clams. Upon finding a gaping oyster the bird plunges its beak between the shells to cut the adductor muscle. This causes the shell to fall open and the oyster is easily obtained. Oystercatchers were hunted to near extinction in the early 1900's (Sandifer et al. 1980) but today the species is considered a common year-round resident. Although this bird is now common, the number of nests observed in the ACE Basin study area is low (Oystercatcher abundance {table icon}) because of anthropogenic disturbance of its nesting habitats.

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Wetland Ecosystems

Impoundments
Impoundments are estuarine or freshwater wetlands which have been diked to create managed bodies of water. Most impoundments in the ACE Basin study area are managed for waterfowl and are characterized by brackish or freshwater vegetation. The waterfowl in impoundments consists of geese (Canada geese); puddle ducks (e.g. mallards, teals, gadwalls, wigeons, and shovelers); and diving ducks (e.g. ring-necked ducks, buffleheads, mergansers, and ruddy ducks). Puddle ducks are the most abundant group of waterfowl. These species preferentially feed on wild rice, spikerush, pondweeds, smartweeds, bulrushes, and wigeon grasses and, therefore, many impoundments are managed for these plant species (see Harvest management of waterfowl ). The Christmas Bird Count (CBC) found that the green-winged teal and the American wigeon (i.e. baldpate) were among the five most abundant species of birds found within the survey area (Christmas bird count {table icon}). About 75% of the survey area is non-forested wetlands that contain numerous impoundments.

Rails, coots, and gallinules are also commonly found in impoundments. The king rail inhabits freshwater impoundments while the clapper rail is restricted to estuarine impoundments. Virginia rails, sora rails, American coots and the common gallinules (i.e. common moorhen) inhabit both estuarine and freshwater impoundments where they feed on snails, insects, fish, and aquatic plants. Herons, egrets, and ibises also utilize impoundments for feeding. The CBC found the white ibis to be the most abundant wading bird in the survey area with the great egret, glossy ibis, and great blue heron also abundant (Christmas bird count {short description of image}).

Other shorebirds that are common in impoundments include yellowlegs, plovers, dowitchers, sandpipers and avocets. The American avocet is a rare winter inhabitant of the ACE Basin study area. This species feeds by sweeping its long bill through shallow water and consuming the aquatic insects and marsh plant seeds that it stirs up (National Geographic Society 1987; Potter et al. 1980). The bald eagle and osprey, although uncommon, both use this habitat as hunting grounds.

Non-Forested Wetlands
The avifauna of palustrine non-forested wetlands contains many of the same species that occur in impoundments and estuarine emergent wetlands. The transitional zone from brackish to freshwater contains a high diversity of vegetation for food and habitat. Ninety-two of the 177 avian species in the ACE Basin study area are estimated to occur within non-forested wetlands. Twenty-one of these species are considered common year-round residents while an additional 25 are common winter residents (Bird habitat {table icon}warning icon). The CBC found that the common grackle and the red-winged blackbird were the most abundant species within the survey area. These birds are both omnivores, but there is a seasonal shift from a diet of mostly insects in the spring and summer to mostly seeds and grains in fall and winter (Bent 1965).

Non-forested wetlands provide nesting grounds for a variety of birds including gallinules, wrens, swallows, red-winged blackbirds, and king rails. The tree swallow is probably the most abundant swallow during the winter while the purple martin is the most abundant summer resident. The purple martin nests in hollow trees and bird houses and forages for insects over open areas such as ponds, rivers, and marshes (Bent 1963a). Other birds such as herons, egrets, and ibises use freshwater wetlands as feeding grounds. Great egrets are a common sight in ACE Basin wetlands. This wading bird nests in mixed species colonies in tall trees near or over water.

Waterfowl are abundant in this habitat because the freshwater vegetation is often preferred over salt marsh vegetation for food. Most waterfowl species such as mallards, teals, gadwalls, and pintails are winter residents and, in general, are present in the ACE Basin study area from September to May. The ring-necked duck is especially abundant here during the winter because of its preference for the seeds of freshwater plants such as waterlilies and watershields.

Several insectivores including the common yellowthroat, marsh wren, barn swallow, and purple martin are common in palustrine wetlands while granivorous species include the swamp, song, and Savannah sparrows. Numerous raptor species are found in non-forested wetlands. Ten of the thirteen hawk species identified by the South Carolina Coastal Hawk Migration Survey inhabit non-forested wetlands (Hawk migration {table icon}). Both the red-tailed and red-shouldered hawks are common year-round residents and marsh hawks and sparrow hawks are the most common winter residents.

southern bald eagleBald eagles are the top predators here, although these birds nest in trees and use the wetlands only for hunting. In 1977, there were only 13 occupied bald eagle breeding areas known to remain in all of South Carolina. Six of the 13 were in the ACE Basin. This remnant population allowed for the recovery of the eagle population to occur far more rapidly then in adjacent states where no nesting eagles remained (Bald eagle nests {short description of image}). The ACE Basin provides high quality nesting habitat with abundant prey, large trees for nesting and protection from disturbance at nest and foraging sites.

Typically, an eagle’s diet is composed of 80% fish, 10% birds, 5% mammals and 5% carrion. The presence of abundant bird prey such as coots, moorhens and ducks, however, results in a greater percentage consumption of birds in the diet. This may have mitigated some of the effects of pesticides, with fish prey more heavily contaminated then birds. The extensive acreage of managed marsh impoundments that occur in the ACE Basin study area and elsewhere in the state, may explain why South Carolina maintained a remnant eagle nesting population.

During the 1998 nesting season, 30 of the 129 occupied breeding areas in South Carolina were in the ACE Basin (Bald eagle nests {short description of image}). While the percentage of nests in the ACE Basin has declined as eagle nesting has repopulated statewide, it still remains one of the high density centers for nesting. Nesting occurs during the winter with the peak of egg laying the last week in December. Winter nesting is adaptive as water clarity is maximum, wintering bird prey are available and shad and herring runs coincide with the maximum energy demands of the chicks in the nest.

Bald eagles can be seen during any month of the year, but are most abundant during the winter. They reach their lowest density during July and August because many birds move north after the nesting season.

Palustrine Forests
Forested wetlands in the ACE Basin study area provide avifauna a wide variety of habitat types. The occurrence of wet and dry tree species and both grassland as well as closed canopy sites contribute to a high diversity of birds (Sandifer et al. 1980). An estimated 132 species of birds can be found in forested wetlands; the highest diversity of any environment in the ACE Basin study area. Of these 132 species, 34 are common year-round residents and 23 are common winter residents. Common year-round residents include omnivores such as the American crow, common grackle, and red-winged blackbird; herbivores such as wood ducks and mourning doves; insectivores such as Carolina wrens, white-eyed vireos, and common yellowthroats; scavengers such as black and turkey vultures; and raptors such as bald eagles, barred owls, red-shouldered hawks, and red- tailed hawks. Common winter residents include American goldfinches, robins, cedar waxwings, dark-eyed juncos, eastern phoebes, hooded mergansers, lesser scaups, song sparrows, and ruby- crowned kinglets.

woodstorkPalustrine forests are important nesting grounds for wading birds such as herons, ibises, and egrets. White ibises which are the second most abundant colonial nesting bird in the ACE Basin study area, nest almost exclusively in wooded swamp habitats (Wading bird nesting habitat {table icon}). Cattle egrets and great egrets also nest in wooded swamps with 71% and 41%, respectively, of the nests occurring in this habitat. In the ACE Basin study area, wood storks also nest exclusively in wooded swamps. These birds are federally endangered and, until 1981, no eggs or young had been reported in South Carolina. Nesting populations of wood storks have steadily increased since 1981 and in 1997, 653 wood stork nests were identified in the ACE Basin study area (Wood stork abundance {graph icon}).

Ten species of birds are closely associated with forested wetlands. Most of these species are warblers which feed on the large number of insects that occur in this habitat. Seven of these species, the blue-winged warbler, golden-winged warbler, Tennessee warbler, Swainson’s warbler, black-throated warbler, gray-cheeked thrush, Louisiana waterthrush, and worm-eating warbler, are rare or uncommon but can be found in forested wetlands of the ACE Basin study area (Bird habitat {table icon}warning icon). The Breeding Bird Survey (BBS) which includes forested wetland habitats identified Swainson’s warbler in 1977, 1993, and 1995. The BBS also found the Kentucky warbler, which is considered a fairly common summer resident of the ACE Basin study area, to be present every year from 1991 to 1996.

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Riverine Ecosystems

The riverine system as discussed here is limited to the open water areas of rivers and does not include adjacent wetland areas. The avifauna of the riverine systems of the ACE Basin study area is made up of species that occur in other habitats and use the rivers for feeding or resting (Sandifer et al. 1980). Species found here forage in the rivers for aquatic plants or animals. Grebes and wading birds hunt for fish either by diving (grebes) or by fishing from shore (wading birds). Shorebirds such as sandpipers and plovers also fish from shore in the rivers for crustaceans, mollusks, fish, and aquatic insects while gulls and terns forage on the rivers for similar prey.

About eleven species of ducks use the river to forage for aquatic vegetation such as pondweeds, wigeon grass, wild rice, eelgrass, and marsh grass. The wood duck is a dominant year-round resident in riverine systems. This species nests on or near water in the natural cavities of dead or live trees (Potter et al. 1980) and young hatch in April or May. Both year-round residents and wintering residents of wood ducks can be found in the ACE Basin study area. Insectivores such as swifts and swallows hunt over the rivers for aquatic insects. The chimney swift is a voracious insectivore which feeds over rivers. This small, dull-colored bird often gathers in large numbers and spends most, if not all, of its day on the wing catching beetles, flies, and ants (Bent 1964; Sprunt and Chamberlain 1970). Osprey

The osprey is the only bird of prey to utilize this habitat extensively. Ospreys can be seen during all months of the year, but are in low numbers during December and January. The osprey not only hunts in the riverine waters for fish but it also commonly nests on dead snags, channel markers, and power line poles in rivers. The osprey is almost exclusively a fish eating species and, like the bald eagle, suffered a dramatic population decline in numbers as a result of pesticide contamination. By the mid 1970’s, it is estimated that the statewide population had declined to 300 nesting pairs. Currently this population has recovered to more than 1,000 nesting pairs. Populations within the ACE Basin continue to increase with nesting concentrated on the Combahee River. Unlike the Charleston Harbor population of ospreys, the birds nesting in the ACE Basin only occasionally build nests on manmade objects. The ACE Basin study area serves as a control that can be used to evaluate the effects of development on the osprey population (Murphy pers. comm.).

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Old Fields

Old field habitats consist of croplands, fields, and pastures along with their adjacent edge communities in which secondary succession is just beginning. Diversity and densities of birds tend to be low in newly abandoned farmlands and to increase as succession proceeds. The edge community supports a high diversity and density of avifauna. The combination of open grasslands, transitional shrubs, and trees provides ideal habitat for many species by providing access to feeding grounds, nearby escape cover, and prime nesting habitat.

hawk flyingSeventy-four birds are estimated to occur in old-field habitats of the ACE Basin study area. Of these, 20 are common year-round residents, 14 are common winter residents, and seven are common summer residents. Many of the birds (e.g. cardinals, mockingbirds, mourning doves, buntings, and sparrows) that occur here fulfill part or all of their dietary needs from the seeds, grains, and fruits that are plentiful in these fields. Others (e.g. Carolina wren, common yellowthroat, brown thrasher, and eastern meadowlark) consume the insects that are feeding in this habitat. Because many old-field birds consume vast numbers of insects, they are extremely beneficial to farmers in insect control. Omnivores common in this habitat include American crow, red-winged blackbirds, and common grackle. The Breeding Bird Survey and the Christmas Bird Count, which both traverse areas containing old field habitats, found that these species were quite abundant.

Eight birds of prey are found in this habitat. Seven of the eleven species of migratory hawks identified on Edisto Island by the South Carolina Coastal Hawk Migration Survey inhabit old-field communities (Hawk migration {table icon}). The red-tailed hawk is probably the dominant raptor in this habitat. This large broad-winged hawk feeds primarily by the perch and wait method of hunting. Food consists primarily of small mammals. Because of the extensive time this species spends perching, it is conspicuous on the landscape and is frequently blamed for the depredations of other species of predators. This is the largest and most common of the broad-winged (Buteo) hawks found in the ACE Basin study area (Murphy pers. comm.).

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Pine Forests

The avian fauna in pine forests of the ACE Basin study area is less diverse than many other habitats. Coastal plain pine forests don’t develop dense understories because of frequent fires as well as poor soil conditions. The lack of a dense understory combined with the low habitat variability in monotypic pine canopy results in a low species diversity. Fifty-two species of birds are estimated to occur in pine forests and almost half are considered common year-round residents. Insect-eaters, generalists, and seed-eaters are represented by warblers, bobwhites, and the brown-headed nuthatch, respectively.

Four species of warblers can be found in pine forests and the pine warbler is most commonly associated with this habitat. Pine warblers build their nests in pine trees and forage for grasshoppers, locusts, moths, beetles, flies, and other insects. The brown-headed nuthatch is a seed-eating species that is most common in pine forests. This species builds its nests in cavities of decaying trees and lines the nest with the sheaths of pine seeds. The nuthatch consumes mostly pine seeds along with some insects (Sprunt and Chamberlain 1970). The bobwhite quail is an omnivore that is abundant in pine forests. Bobwhites are a popular game bird in the ACE Basin study area and are hunted extensively (See related subsection: Hunting: Bobwhite Quail.) This species builds its nest in areas where vegetation is dense and provides abundant cover. Bobwhites eat a myriad of foods including seeds, insects, fruits, leaves, spiders, crustaceans, and tubers (Bent 1963b).

Woodpeckers are also abundant in this habitat, with the red-bellied being most abundant. The Breeding Bird Survey found the red-bellied woodpecker (Woodpecker abundance {short description of image}) was the most abundant woodpecker species in upland areas. Seven birds of prey can be found in pine forests. The screech-owl, which often builds its nest in woodpecker holes, is a dominant owl species in this habitat (Sandifer et al 1980). Both red-shouldered and red-tailed hawks were found to occur in the upland areas surrounding Walterboro.

Pine-Hardwood Upland Forests
Pine-hardwood forests in the ACE Basin study area have more bird species than the other upland communities. These forests have extensive subcanopy and understory growth that is not found in either pine forests or in old-field communities (see the Plants: Upland Community ). The addition of the subcanopy and understory vegetation greatly augments the habitat types available and, therefore, more birds can be found here (Sandifer et al 1980). As with many other forested habitats, insectivores are common in mixed upland forests. Along with warblers and woodpeckers, the Carolina wren, tufted titmouse and white-eyed vireo are abundant (Insectivores {short description of image}). The Carolina wren is the state bird of South Carolina and is found in a variety of habitats. This species will nest almost anywhere a suitable nook or cavity is available including natural cavities, birdhouses, and mailboxes. Carolina wrens feed on a variety of insects and are, therefore, beneficial to farmers. Common granivores in this habitat include the mourning dove and the American goldfinch. Both of these species subsist almost entirely on seeds. The mourning dove is an important game species and is a year-round resident of the ACE Basin study area. The American goldfinch is a winter resident that consumes the seeds of sweetgum trees as a major part of its diet (Martin et al. 1951). The same species of raptors occur in mixed forests as in the pine forests. Dominant scavengers are the black and turkey vultures while the great-horned owl is the top predator (Sandifer et al 1980).

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Conservation Issues

wild turkeyIndiscriminate hunting for plumage or sport around the 1900's had devastating effects on many species of birds. The great egret, the snowy egret, and least tern were hunted almost to extinction for their plumage while birds such as the wild turkey and wood duck were over-exploited by sport hunting. Conservation efforts that began in the 1800's have resulted in the protection of many of these exploited birds. The Endangered Species Act of 1973 was established to protect species that are in danger of becoming extinct. All migratory birds are now protected by federal law as are nonmigratory hawks and owls. These birds can not be killed legally except during regulated hunting season on specific species (Potter et al. 1980).

Unregulated pesticide use has also resulted in population declines of bird species. DDT, which was used in the United States prior to 1972, was particularly harmful because it was applied for a wide variety of purposes and its toxicity persists long after application. Ospreys, wading birds, and bald eagles are among the species of birds that were affected by pesticides such as DDT. These birds are generally higher level predators that are feeding on organisms that have bioaccumulated harmful pesticides. As these birds bioaccumulate pesticides, both lethal and sublethal effects can result. Birds can die from lethal effects or from weakness associated with the pesticides which causes increased susceptibility to disease or predators. One of the most common sublethal effects associated with pesticide use is thinning of eggshells. Thin eggshells are more likely to break, thereby killing the young. Obviously, when the young die, the population declines greatly. Through more strict regulations on pesticide use, bald eagles, pelicans, and ospreys, as well as many other bird species are slowly recovering.

The most serious conservation issue for birds of the ACE Basin study area is habitat destruction. Although much of the ACE Basin study area is protected from development, there are still concerns. The conversion of upland communities into pine plantations and croplands has limited habitat diversity resulting in a subsequent decline in species diversity. Development of the beach communities has decreased the nesting habitat available to shorebirds. Redivergence of river channels has destroyed several bird keys that are important to colonial waterbirds. Habitat destruction in other regions can significantly affect species in the ACE Basin study area. As discussed above, many birds are migratory and use the ACE Basin study area only for a part of the year. For example, songbirds such as the summer tanager migrate from their summer breeding grounds (which includes the ACE Basin study area) to Latin America for the winter. As nesting habitat (i.e. forests) in the ACE Basin study area and winter habitats in Latin America are converted to other land uses songbird populations decline. Recent declines in songbird population have been noted both nationally and in the ACE Basin.

To ensure the health of the avifauna, conservation groups must continue to strive to protect species from harm due to over-hunting, environmental pollution, and habitat loss. Careful control of hunting and pesticide use can protect species to a degree, but habitats must be preserved. Because every species has different needs, the effect of development on each species found in a habitat must be examined to ensure the continued existence of the population.

NEXT SECTION: Mammals



Author

L. Zimmerman, SCDNR Marine Resources Research Institute



References

Bent, A. C. 1963a. Life histories of North American flycatchers. Dover Publishing Inc., New York, NY.

Bent, A. C. 1963b. Life histories of North American gallinaceous birds. Dover Publishing Inc., New York, NY.

Bent, A. C. 1964. Life histories of North American cuckoos, goatsuckers, hummingbirds and their allies. 2 Parts. Dover Publishing Inc., New York, NY.

Bent, A. C. 1965. Life histories of North American blackbirds, orioles, tanagers and allies. Dover Publishing Inc., New York, NY.

Bent, A. C. 1968. Life histories of North American cardinals, grosbeaks, buntings, towhees, finches, sparrows, and allies. Smithsonian Institution Press, Washington, DC.

Campbell, N. A. 1993. Biology. 3rd Edition. Benjamin/Cumming Publishing Company Inc., Redwood City, CA.

Martin, A. C., H. S. Zim, and A. L. Nelson. 1951. American wildlife and plants: A guide to wildlife food habits. Dover Publishing Inc., New York, NY.

Murphy, T. undated personal communication. South Carolina Department of Natural Resources, Wildlife and Freshwater Fisheries Division.

National Geographic Society. 1987. Field guide to birds of North America. Second edition. National Geographic Society, Washington, DC.

Potter, E. F., J. F. Parnell, and R. P. Teulings. 1980. Birds of the Carolinas. University of North Carolina Press, Chapel Hill, NC.

Sandifer, P. A., J. V. Miglarese, D. R. Calder, J. J. Manzi, and L. A. Barclay. 1980. Ecological characterization of the sea island coastal region of South Carolina and Georgia. Vol. III: Biological features of the characterization area. U.S. Fish and Wildlife Service, Office of Biological Services, Washington, DC. FWS/OBS-79/42.

Sprunt, A., Jr. and E. B. Chamberlain. 1970. South Carolina bird life. University of South Carolina Press, Columbia, SC.

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