U.S. Fish & Wildlife Service

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Division of  Migratory Bird Management

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Waterfowl Breeding Population and Habitat Survey
Traditional Survey

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. 2013. Waterfowl population status, 2013. 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).

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 Ornithologistsí 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

 

Year

Survey year

Stratum

Stratum number

Transect

Transect number

Segment

Segment number

AOU

American Ornithologistsí 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)

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