LIMITATIONS
The spatial sampling design and timing of the survey are focused
primarily on mallards, an early-nesting species that is important in the
annual duck harvest of both the United States and Canada. The survey has
known limitations for species which breed in significant densities well
beyond the strata boundaries of the survey such as green-winged teal and
many sea ducks. Likewise, the timing of the survey, while near optimal for
mallards, may be too early for some diving ducks and sea ducks and may
result in double counting of birds during migration, or in counting birds
prior to reaching their breeding grounds terminus area.
POINT OF CONTACT
Emily Silverman
Population & Habitat Assessment
Branch
Division of Migratory Bird Management, USFWS
11510 American Holly Drive
Laurel, MD 20708
voice mail: (301) 497-5801
fax: (301) 497-5871
emily_silverman@fws.gov
LITERATURE
CITED
Smith, G.W. 1995. A critical review of the
aerial and ground surveys of breeding waterfowl in North America. Biological
Science Report 5, National Biological Service, Washington, D.C. 252pp.
U.S. Fish and Wildlife Service. 2014.
Waterfowl population status, 2014. U.S. Department of the Interior, Washington,
D.C. USA.
PURPOSE
The Waterfowl Breeding
Population and Habitat Survey was initiated experimentally in 1947 and
became operational in 1955. It has been conducted every year since. The
primary purpose of the survey is to provide information on spring population
size and trajectory for certain North American duck species. These data
are used extensively in the annual establishment of hunting regulations
in the United States and Canada and provide long-term time series important
in researching bird-environment relationships critical to effective conservation
planning for waterfowl.
PROCEDURES
Survey procedures and analytical methods for the Waterfowl Breeding Population
and Habitat Survey are described in detail by Smith (1995). The U.S. Fish
and Wildlife Service and the Canadian Wildlife Service in cooperation
with others have conducted an annual survey of breeding waterfowl throughout
central Canada, the north-central United States, and Alaska since 1955.
The area comprises more than 50 strata delineated according to habitat
differences and political boundaries. Since 1990 strata delineated in
important duck breeding areas in eastern Canada and the northeast United
States have been progressively phased into this long running wildlife
survey.
Within strata, ducks
are counted by two-person aerial crews while flying fixed-wing aircraft
along established transect lines approximately 50 m above ground level.
Transects are 400m wide and divided into segments, each roughly 29 km
in length. Aerial observers do not count lone hen ducks. Ponds are counted
only by the observer, not by the pilot-observer to reduce pilot workload.
In prairie and parkland strata, where ground transportation networks and
access is good, ground crews (initiated in 1961 for Canada and 1974 in the United States) survey a sub-sample of aerial segments. Ground
counts are used to compute visibility correction factors that adjust the
counts of each aerial crew for each species to account for birds not observed
from the air.
Ground crews record
data in a manner identical to aerial crews, except that ground crews also
record lone hens of redheads (Aythya americana), scaups (Aythya marila
mariloides and Aythya affinis), ring-necked ducks (Aythya collaris), and
ruddy ducks (Oxyura jamaicensis jamaicensis). Since the establishment of the ground crews and unlike the aerial crew,
the ground crew also counts all ponds within the entire transect width
and records the side of the transect that each pond is observed on. This
enables aerial pond data to be compared to the appropriate ground count
when computing visibility correction factors. In boreal strata, where
ground transportation is difficult, visibility correction factors are
determined from a double sample of segments by helicopter. The high cost
of helicopter operation currently prohibits extensive double sampling
in boreal strata. The total number of birds in each stratum is estimated
by the product of the density observed by the aerial crew, the visibility
correction factor, and the area of the stratum.
DATABASES
Two databases derived from the Waterfowl Breeding Population and Habitat
Survey are available online through this website.
These are the strata estimates database and the segment-level count database.
The strata estimates database includes species- and year-specific estimates
and standard errors of absolute waterfowl abundance for individual survey
strata. Users querying this database will need to specify the time interval,
species, and geographic region of interest. Pond estimate and segment counts are available dating back as far as 1955, however, it is important to note that the status report only presents pond numbers dating back to when the ground crews became operational and the collection of pond data became a requirement (Canada, 1961 and U.S., 1974). As noted directly above this
enables aerial pond data to be compared to the appropriate ground count
when computing visibility correction factors.
Note: NA/NULL values
VCF's are assigned at the level of the
crew area (i.e., to groups of strata). NA values are reported for the VCF
when the species was seen in NONE of the strata within the crew area. If
the species was seen in one or more strata within the crew area, a VCF is
assigned to all strata in the area, including strata with zero counts for
that species (i.e., some population estimates = 0 have a VCF and some have
NA , depending on whether the species was present in the crew area or
not).
Under Maintenance - Segment data requests can be filled by the Data Administrator. The segment-level
count database records raw count data for the Waterfowl Breeding Population
and Habitat Survey at the level of sample segment. The 18-mile long segment
is the primary unit on which waterfowl are counted and summarized for
this survey. Records in this database include year, strata, transect,
and segment identifiers, species, and the number of single drakes, pairs,
and mixed sex flocks counted by the aerial survey crew. Users querying
this database will need to specify time interval, species, geographic
region, and count category (singles, pairs,
or groups).
DOWNLOADABLE
FIELD DEFINITIONS
Field
Name |
Field
Definition |
Strata
Estimates Database |
|
Year |
Survey
year |
Stratum |
Stratum
number |
AOU |
American
Ornithologists’ Union Species Code |
Species |
Species
common name |
Pop |
Population
estimate for stratum |
Sepop |
Standard
error of stratum population estimate |
Vcf |
Visibility
correction factor used in estimation |
Sevcf |
Standard
error of the VCF used in estimation |
VCF Computation Method |
Methods
used to compute VCFs (2008-present) |
Imputation Codes |
Indicator variables used to determine if imputed data were used in estimation (1955-2007) |
Segment
Count Database (Under Maintenance) |
|
Year |
Survey
year |
Stratum |
Stratum
number |
Transect |
Transect
number |
Segment |
Segment
number |
AOU |
American
Ornithologists’ Union Species Code |
Sngl |
Number
of lone drakes (dimorphic species) or unknown sex singles (monomorphic species) counted on a segment |
Pair |
Number
of pairs counted on a segment |
Open |
Number
of birds counted in mixed sex groups on a segment (or ponds if selected in query) |
Return
to Waterfowl Breeding Population and Habitat Survey
Homepage
|