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Range
In North America, Mallard breeds from north-central and
southwestern United States north to northern Alaska and the
Northwest Territories excluding the Maritimes and eastern
Arctic. Winters mainly from southern Canada south to central
Mexico; also on the Pacific coast north to the Aleutian
Islands. Also resident in Eurasia.
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Status
Common to very abundant
migrant. In winter, common to very abundant on the coast;
locally common to abundant in the southern interior; locally
rare to uncommon in the northern interior. Widespread
breeder.
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Status
Change
No change.
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Nonbreeding
The Mallard is the most
abundant and widely distributed duck in British Columbia and
has been recorded from sea level to 3,000 m elevation. It
occurs virtually everywhere open water is present. Shallow
marshes are preferred, but Mallards also frequent lakes,
rivers, sloughs, estuaries, ponds, ditches, wet fields, and
coastal marine waters. In urban environments, ponds,
puddles, and other damp areas attract Mallards, especially
in parks. On the south coast, the Mallard loafs on estuaries
and offshore in bays and inlets. It forages on nearby
farmlands, preferring flooded fields to dry fields (Hirst
and Easthope 1981), as well as in tidal marshes and
estuaries (Eamer 1985). Salmon spawning rivers are used in
all coastal areas in autumn and winter. In the interior,
preferred habitats include marshes, wet and dry fields, and
lakeshores.
The Mallard is an extremely
early spring migrant; in the interior, it is frequently seen
on the first open waters of lakes and rivers. The movement
begins in the south in mid-February and continues in the
north through early May. Spring flocks are small10 to
200 birds. Post-breeding males begin to flock together for
the summer moult by mid-May in the south and late June in
the north. In autumn, migration begins in late August and
continues through December, and is the most protracted
movement of all the dabbling ducks. Flocks of up to several
thousand birds occur. Mallards will remain as far north as
conditions permit. The major influx of migrants into
southern British Columbia in some years may not occur until
November.
In winter, tens of thousands
occur along the coast; the major concentration is on the
Fraser River delta (Butler, R.W. and Campbell 1987). At
least 39,000 birds have wintered in the southern coastal
area (Appendix 2) which is about 2% of the Pacific Flyway
population of 1,970,000 as indicated by Bellrose (1976) and
at least twice the wintering numbers reported by the same
author. In the interior, much smaller numbers winter as far
north as the Peace River; in recent years, however, several
thousand have wintered near Vernon. Wintering populations
increased dramatically in the interior after grain farming
was initiated in the early 1930s (Munro, J.A. 1943). Near
urban centres, supplemental feeding of Mallards by the
general public has greatly influenced the winter
distribution of the species in British Columbia.
Eamer (1985) found that
dabbling ducks, primarily Mallard and American Widgeon,
moved between coastal sites and flooded fields depending on
the degree of flooding in the fields and the presence or
absence of freezing temperatures. She believes that single
sites should not be considered in isolation, but rather as
part of a wetlands complex.
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Breeding
BREEDING: The Mallard breeds in
wetlands throughout British Columbia from sea level to 1,300
m elevation. Habitats include sloughs, marshes, lakes,
swamps, islands, and riparian woodlands. In urban and rural
environments, parks, golf courses, ditches, agricultural
fields, vacant lots, and private yards are used wherever
fresh water is near.
The Mallard is a solitary
breeder, but loose aggregations of up to 14 nests have been
found on small islands near Creston. The centre of abundance
is in the Chilcotin-Cariboo. The breeding season is
unusually long and may extend from February to November on
the south coast.
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Nests: 
Nests were usually situated on
dry land near water. Major habitats for 235 nest sites
included marshes (37%), woodlands (15%), lake edges (14%),
islands (12%), pastures (8%), and riverbanks (4%). Of 22
nests, 17 were within 40 m of water; 5 others were from 200
m to 1.6 km from water.
Most nests (88%; n=224) were
shallow depressions in the ground filled with various
quantities of down and loose accumulations of leaves,
grasses, needles, sedges, or mosses. In other situations,
nests were constructed differently. For example, nests on
logs, among flooded willow clumps, in tree crotches, and on
artificial platforms (7%; n=224) were heaps of aquatic
plants and other vegetation. Nests in cattail beds were
down-filled platforms of interwoven cattail
stems.
Most nests (76%; n=224) were
well concealed by vegetation, including grasses (22%),
brushy thickets (16%), saplings (9%), cattail and rushes
(8%), roots and logs (6%), and single shrubs (5%).
Twenty-one per cent of the nests were situated at the bases
of trees in relatively exposed situations. Six nests were
found in trees: three in willow crotches, two in large
natural cavities 2 to 3 m above ground, and one in an
American Crow nest 4 m above ground.
One nest site, situated in a
woodland at Cluculz Lake, was occupied for six consecutive
years. A nest at Milch Lakes was rebuilt on top of a
recently flooded nest, while a nest in Howe Sound was within
a Glaucous-winged Gull colony. Two nests on Reifel Island
contained Ring-necked Pheasant eggs.
Eggs:
Dates for 242 clutches ranged
from 28 February to 10 July with 50% recorded between 29
April and 27 May. Records of downy young on 20 March and 15
November indicate egg laying could occur as early as 15
February and as late as 15 October.
Sizes for 355 clutches ranged
from 1 to 24 eggs (1E3, 2E-5, 3E-4, 4E-9, 5E-14, 6E-23,
7E-37, 8E-62, 9E-69, 10E-54, llE43, 12E-19, 13E-5, 14E-5,
l9E-1, 21E-1, 24E-1) with 52% having 8 to 10 eggs. Clutches
of 19, 21, and 24 eggs are likely the product of at least 2
females. Incubation period is 26 to 30 days, with a 28-day
average (Girard 1941).
Young:
Dates for 1,111 broods ranged
from 20 March to 15 November with 53% recorded between 22
May and 28 June. Downy young (Class I) on 15 November (lower
Fraser River valley) would not fledge until early January;
it is not known if they survived. Sizes for 1,987 broods
ranged from 1 to 22 young (1Y-42, 2Y-97, 3Y-157, 4Y-193,
5Y-261, 6Y-310, 7Y-266, 8Y-235'9Y149, 10Y-128, llY-60,
12Y-51, 13Y-11, 14Y-9, 15Y-4, 16Y-5, 17Y-2 18Y-4, l9Y-1,
21Y-1, 22Y-1) with 54% having 5 to 8 young. Fledging period
ranges from 42 to 60 days depending on the latitude of
breeding (Hochbaum 1944; Lensink, C.J. 1954).
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Remarks
Eamer (1985) discusses winter
habitat and foods of the Mallard on southeastern Vancouver
Island. She found that the Mallard selects a wide variety of
food types from the estuarine marshes and marine deltas
including algae (Ulva sp., Enteromorpha sp.),
marine snails, insect larvae, Pacific silverweed roots and
stems, sedge achenes, and other assorted seeds. Seeds,
however, did not dominate the diet to the extent reported in
Burgess (1970) for Mallards on the Fraser delta.
The Mallard is the single most
important game duck in British Columbia, and hunting seasons
are planned around its migration and seasonal distribution.
About 100,000 (55% of the duck harvest) are taken in British
Columbia each year.
See Anderson, D.R. and Henny
(1972), Anderson, D.R. et al. (1974) and Pospahala et al.
(1974) for summary information on population ecology of the
Mallard in North America.
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Located
at:
675 Belleville Street,
Victoria, British Columbia,
CANADA

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