Marbled murrelet


The marbled murrelet is a small seabird from the North Pacific. It is a member of the auk family. It nests in old-growth forests or on the ground at higher latitudes where trees cannot grow. Its habit of nesting in trees was suspected but not documented until a tree-climber found a chick in 1974, making it one of the last North American bird species to have its nest described. The marbled murrelet has declined in number since humans began logging its nest trees in the latter half of the 19th century. The decline of the marbled murrelet and its association with old-growth forests, at least in the southern part of its range, have made it a flagship species in the forest preservation movement. In Canada and Alaska, the declines are not so obvious because populations are much larger and the survey techniques have not had sufficient power to detect changes.

Description

The marbled murrelet is a small, chunky auk with a slender black bill. It has pointed wings and plumage that varies by season. The non-breeding plumage is typically white underneath with a black crown, nape, wings and back. The bird closely resembles its closest relative, the Long-billed murrelet; in fact, these species were considered conspecific up until 1998. In breeding plumage, both have a brown mottled body and face. The Long-billed has a pale white throat, lacking in the Marbled. In winter plumage, the Marbled murrelet has a white neck collar, absent in Long-billed. The Marbled murrelet is shorter-billed and slightly smaller than the Long-billed murrelet.

Behavior

Diet and feeding

The marbled murrelet feeds at sea both in pelagic offshore areas and inshore in protected bays and fiords. The bird has not been known to wander from the Pacific coast of North America, all inland and eastern Brachyramphus records being of the closely related long-billed murrelet.
Marbled murrelets feed below the water surface on small fish and invertebrates. Some principal foods include sand lance, Pacific herring, capelin, shiner perch, and the invertebrates Euphausia pacifica and Thysanoessa spinifera.
Marbled murrelets often forage in pairs but do not feed in large flocks as do other alcids. Loose aggregations of 500 or more birds occasionally occur in winter. Subadults feed singly; but in early July, when pairs of adults are still feeding young, mixed flocks begin to form. Marbled murrelets feed during the day and at night.

Breeding

The nesting behavior of the marbled murrelet is unusual, since unlike most alcids it does not nest in colonies on cliffs or in burrows, but on branches of old-growth and mature conifers such as western hemlock, Sitka spruce, Douglas-fir and coastal redwood, as far as 80 km inland. It lays one egg on a platform of lichen or moss on these branches. In northern populations, murrelets nest on the ground among rocks, as do other related murrelet species. The egg is incubated for a month, then fed for around 40 days until the chick is able to fledge. Adults fly from ocean feeding areas to inland nest sites, mostly at dusk and dawn. They feed nestlings at least once and sometimes twice per day or night. Usually only one fish is carried to the young. The chick then leaves the nest and flies unaccompanied to the sea. Breeding success is low and chick mortality high.
Marbled murrelets do not breed until they are at least two years old. Marbled murrelets nest from mid-April to late September. Peak activity occurs from mid-June to late July in California, and the second week of July to mid-August in Oregon. Marbled murrelets are semicolonial in nesting habits. Two nests found in Washington were located only 150 feet apart. Not all mature adults nest every year. Marbled murrelets lay only one egg.
Nestlings fledge in 28 days. Young marbled murrelets remain in the nest longer than other alcids and molt into their juvenile plumage before leaving the nest. Fledglings fly directly from the nest to the ocean.

Habitat and distribution

Marbled murrelets occur in summer from Alaska's Kenai Peninsula, Barren islands, and Aleutian Islands south along the coast of North America to Point Sal, Santa Barbara County, in south-central California. Marbled murrelets winter mostly within the same general area, except that they tend to vacate the most northern sections of their range, especially where ice forms on the surface of the fiords. They have been recorded as far south as Imperial Beach of San Diego County, California.

Habitat

Marbled murrelets are coastal birds that occur mainly near saltwater within 1.2 miles of shore. However, marbled murrelets have been found up to 59 miles inland in Washington, 35 miles inland in Oregon, 22 miles inland in northern California, and 11 miles inland in central California. Over 90% of all marbled murrelet observations in the northern Washington Cascades were within 37 miles of the coast. In Oregon, marbled murrelets are observed most often within 12 miles of the ocean. Many marbled murrelets regularly visit coastal lakes. Most lakes used by marbled murrelets are within 12 miles of the ocean, but a few birds have been found at lakes as far inland as 47 miles. All lakes used by marbled murrelets occur within potential nesting habitat.

Nesting habitat

From southeast Alaska southward, marbled murrelets use mature or old-growth forest stands near the coastline for nesting. These forests are generally characterized by large trees, a multistoried canopy, moderate to high canopy closure or an open crown canopy, large snags, and numerous downed snags in all stages of decay. Marbled murrelets tend to nest in the oldest trees in the stand. In Oregon, forests begin to exhibit old-growth characteristics at about 175 to 250 years of age. Moss, on which marbled murrelets nest, forms on the limbs of Douglas-fir that are more than 150 years old.
The only four marbled murrelet tree nests found before 1990 shared the following characteristics: located in a large tree with an open crown structure, on a moss-covered limb that is camouflaged, partially shaded, and approximately horizontal with a diameter of at least 14 inches, and located within the middle or lower part of a live crown. However, Marshall stated that because of their low aerial buoyancy marbled murrelets often nest high in the treetops or on steep slopes. Habitat must be sufficiently open to allow for easy flight. All marbled murrelet nests found in Washington, Oregon, and California were located in old-growth trees that ranged from 38 inches d.b.h. to 210 inches d.b.h. with a mean of 80 inches d.b.h. Nests were located high above the ground and had good overhead protection but allowed easy access to the exterior forest. It was initially believed that marbled murrelets might use the same nest in successive years but there has been little evidence of this.
Stand size is also important in nest sites. Marbled murrelets more commonly occupy stands greater than 500 acres than stands less than 100 acres. However, marbled murrelets may nest in remnant old-growth trees or groves that are surrounded by younger trees. In California, marbled murrelets are usually absent from stands less than 60 acres in size. In Washington, marbled murrelets are found more often when old-growth and mature forests make up over 30% of the landscape. Fewer marbled murrelets are found when clearcut and meadow areas make up more than 25% of the landscape. Concentrations of marbled murrelets offshore are almost always adjacent to old-growth or mature forests onshore, although marbled murrelets may not use the interior of dense stands.
Where large trees are absent in the northern parts of marbled murrelet range, marbled murrelets nest in depressions on the ground, in rock cavities on the ground, or on rock outcrops. Marbled murrelets are both ground nesters and tree nesters where forests and treeless areas meet.

Plant communities

In northern regions where coniferous forests nest sites are unavailable, marbled murrelets occupy alpine or tundra near the ocean. In Washington and Oregon, marbled murrelets commonly nest in Douglas-fir dominated stands. They also select stands dominated by mountain hemlock, western redcedar, and Sitka spruce for nesting. In California, nests are most often located in redwood dominated stands with scattered Sitka spruce, western hemlock and Douglas-fir. Marbled murrelets also occur in stands dominated by Port-Orford-cedar.

Foraging habitat

Marbled murrelets forage in the ocean near shore and in inland saltwater areas such as bays, sounds, and saltwater passageways. Some also forage on inland freshwater lakes. Flocks of 50 or more birds have been observed near freshwater lakes. Subadults occur at sea throughout the summer. Marbled murrelets feed within 1,640 feet of shore.

Winter habitat

Marbled murrelet winter habitat is the same as the nesting and foraging habitat. During the winter marbled murrelets use inland old-growth or mature sites for roosting, courtship, and investigating nest sites. The use of inland lakes during the nonbreeding season occurs in conjunction with visits to nesting areas.

Predators

s and common ravens prey on marbled murrelet eggs and nestlings.

Marbled murrelets and humans

The marbled murrelet is considered globally endangered, with some evidence of decline across its range over the last few decades. The biggest threat to the marbled murrelet was long considered to be loss of nesting habitat to logging. Additional factors including high predation rates due to human disturbances and climate-driven changes in ocean conditions are also considered important now.
Scientists at Redwood National Park have established a connection between human presence in marbled murrelet territory and corvid predation of marbled murrelet chicks. Corvid populations, such as Steller's jays, crows, and ravens, are expanding into old-growth forests. Lured by food scraps left by campers and hikers, with increased access aggravated by the patchwork forests created by industrial logging, corvids more frequently discover marbled murrelet nests in areas where these predator species were not previously found.
The marbled murrelet populations in Washington, Oregon and California were listed as threatened in 1992 by the U.S. Fish and Wildlife Service due to concerns about loss of nesting habitat, entanglement in fishing gear and oil spills. The Canadian population was declared "nationally threatened" in 1990. The status of Alaskan populations is currently under review. The species became a flagship species in efforts to prevent the logging of old-growth forests along the Pacific coast from California to Alaska.