Level II (Monitoring)
The
action and focus for these species is monitoring (M). Declining population trend and habitat loss
are not known to be significant at this point.
Includes species of which
Primary Habitat Type: Wetlands and Aquatic
|
SPECIES & STATUS |
VEGETATION COMPOSITION |
VEGETATION STRUCTURE |
ABIOTIC FACTORS |
LANDSCAPE FACTORS |
SPECIAL FACTORS |
|
Common
Loon (COLO) Gavia immer Level
II M |
~Grassy
shorelines and islands, including grasses, sedges, and rushes |
~Territories
usually include an area of shallow water with emergent vegetation ~Lakeshore
at least partially forested |
~Requires
lakes of ≥10 acres; nesting success is poorer on lakes that are <25
acres ~Water
clarity (minimum visibility of 3 to 4 feet) is important, as loons are visual
predators ~Water
depth >6 feet to prevent winter kill of fish ~Lakes
that remain ice-free for ≥4 months to allow young to fledge ~ ~Steep
slope adjacent to shoreline for an underwater approach to the nest |
~Territory
may range from 10 to 500 acres ~Nest
at elevations between 6,000 and 8,000 feet |
~Sensitive
to human disturbances and water level fluctuations ~Requires
abundant populations of small to mid-sized fish ~Strong
fidelity to breeding territory ~Will
use artificial nesting platforms ~Winters
south to northern |
Found on lakes across most of
Population Objectives
1) Breeding
Bird Survey (BBS) data from 1968 through 2002 are inadequate to determine
population trends for the Common Loon in
Habitat
Objectives
1) Maintain the suitability of currently used Common Loon nesting territories.
2) Protect large, clear, deep lakes throughout the state from habitat degradation.
3) Maintain water quality to sustain substantial populations of small to mid-sized fish as a food source for Common Loons.
Recommendations
1) Protect all current and traditional Common Loon nesting sites from development and degradation. Because loons exhibit strong year-to-year fidelity to previous nest sites, there is a high probability that they will reuse nests and nurseries if these areas are not developed or degraded. When possible, two or three alternate sites with characteristics of preferred nesting areas should be protected on each breeding lake. Small islands should receive complete protection from development. Undeveloped buffer zones of at least 500 feet (150 m) should be left on either side of nest sites and nursery areas.
2) Protect all areas with characteristics suitable for nesting and chick rearing, even if actual use has not been documented.
3) Maintain vegetation buffer zones to block
siltation, pesticide, and fertilizer runoff into lakes.
4) Maintain stable water levels throughout the nesting season in lakes where Common Loons are breeding. Rising water levels can flood nests and, although small drawdowns may be acceptable if distances between nests and the water's edge are not greatly increased, significant lake level subsidence may cause nest desertion or loss of newly-hatched chicks.
5) Avoid disturbing nesting areas, as loons are very sensitive to human disturbance. During times of human intrusion, incubating loons slip off nests, swim underwater, and emerge at a distance, which leaves the nests open to predation. During disturbances after hatching, chicks are dropped off the adult's back, and are left near the shore, where they may be vulnerable to predation.
6) Restrict access to Common Loon nesting territories during the breeding season. Limit or prohibit activities such as boating, fishing, swimming, camping, and picnicking near nest sites and in nursery areas. In some cases, posting signs to discourage visitors may be effective. However, signs may also draw attention to nesting sites and may be ineffective when enforcement is not possible. In such cases, efforts to educate the public may be the most reasonable method of reducing disturbance.
7) Educate the public about the natural history and conservation needs of loons. Most human-related loon problems stem from ignorance, not intent. Public education can include posters and information at marinas and other lake access points; informational brochures; press releases; and lectures, slide programs, and other presentations. Visitors can be required to attend an educational program before entering a wilderness or recreational area with breeding loons.
8) Establish boat engine horsepower limitations and/or speed limits on lakes where Common Loons are breeding, and strictly enforce boating restrictions. Motorboats and personal watercraft (e.g. jet skis) produce waves that can destroy nests and create disturbances that can cause egg or chick loss.
9) Consider known loon nest sites and nesting territories when establishing new campgrounds or campsites. Close present campsites or campgrounds near known loon nesting sites and designate specific campsites well away from nesting loons. Since loons prefer to nest on small islands when they are available, camping should be prohibited on islands, and other uses of islands should be discouraged or, if necessary, prohibited.
10) Consider installing and maintaining artificial nest platforms where fluctuating water levels or the lack of suitable nest sites is limiting Common Loon reproduction. Artificial nest platforms may improve nesting success on lakes that lack natural islands, have poor shoreline nesting habitat, or have a history of low productivity. Platforms rise and fall with water levels and can counteract extreme fluctuations on lakes where loons are not considered in water management plans. Platforms alone are unlikely to induce nesting on unoccupied lakes or territories, and should not be viewed as an easy alternative to the protection of natural nest sites. Artificial nest platforms should not be used where loons are already nesting successfully or where natural nest sites are already available, because they require yearly maintenance, increase dependence on long-term human interest, and attract human attention.
11) Construct artificial nest platforms of five 6- to 8-foot (1.8- to 2.4-m) cedar logs, approximately 8 inches (20 cm) in diameter. Notch the logs at both ends, shape them into a square frame with one cross-log, and join them with #20 galvanized spikes. Staple a 5x5-foot (1.5x1.5 m) piece of heavy plastic snow fencing mesh to the bottom of each frame, wrapping it halfway up the sides from underneath, and making sure there are no protrusions or wild ends that might injure a bird. Attach 3/16-inch (0.5-cm) wire cable to two opposite corners of the raft with cable clamps and secure the cables to two cement block anchors. Fill the raft with 4 to 6 bushels of duff, loose leaves, twigs, and roots, and plant it with low-growing vegetation indigenous to the natural nesting area. Because loons begin nesting very soon after ice-out, install nesting platforms within 2 weeks after ice-out. Place platforms in areas of minimal human disturbance, out of the direct path of prevailing summer winds and waves, in 10 to 30 feet (3 to 10 m) of water and approximately 100 to 165 feet (30 to 50 m) from shore. Completed platforms may last for 3 or 4 years, but in some cases, especially in unprotected locations, they may blow to shore during the spring or fall and have to be pulled back into the lake or replaced.
Primary
Habitat Type: Aquatic
|
SPECIES & STATUS |
VEGETATION COMPOSITION |
VEGETATION STRUCTURE |
ABIOTIC FACTORS |
LANDSCAPE FACTORS |
SPECIAL FACTORS |
|
American
White Pelican (AWPE) Pelecanus erythro-rhynchos Level
II M |
~Prefers
open areas of annual grasses and forbs, shrubs, ~Prefers nonvegetated areas
for nesting |
~Nests
on flat islands without vegetation >3 feet or other tall obstructions |
~Breeds
on large freshwater lakes ~Requires
islands isolated from mammalian predators for nesting ~Prefers
gravel or sandy, unconsolidated substrates for nesting |
~Adults
may travel to lakes, rivers, and marshes >50 miles away from the nest site
to feed |
~Nests
colonially and is highly social ~Very
sensitive to human disturbance during nesting ~Nest
site tenacity between years is low ~Winters
south through lowlands to |
1) Determine statewide population trend data by implementing “Monitoring Wyoming’s Birds: The Plan for Count-based Monitoring”.
2) Breeding Bird Survey (BBS) data from 1968 through 2002
indicate American White Pelicans have been detected on 31 BBS routes in
a) Maintain American White Pelicans on the 31 BBS routes on which they were observed (Figure 23).
b) Maintain the average number of individuals observed per route over the past 5 years at a level equal to or above the average number of individuals observed during all years the route was run.
3) Maintain a minimum of two
nesting colonies in

Figure 23. Bold lines indicate Breeding Bird Survey routes on which American White Pelicans have been observed from 1968 through 2002.
2) Maintain substantial populations of fish as a food source for American White Pelicans.
1) Minimize water level fluctuations during the nest-building through fledging stages of American White Pelicans. Rising water levels can flood nests and lake level subsidence may connect islands to the lakeshore, exposing eggs or young to mammalian predators.
2) Protect any colony sites currently in use, regardless of the size of the site or the number of pelicans present.
3) Protect all remaining suitable aquatic habitat in the state. The success of American White Pelicans depends, in part, on their flexibility in choosing nesting areas. This makes protection of all suitable lakes and islands important because pelicans may use a particular site only occasionally, but when they do, it may be their only chance of nesting success.
4) Maintain ample foraging areas within range of colonies. Protect foraging habitat from widespread permanent flooding or drainage.
5) Avoid disturbing nest sites during the breeding season, as colonies are very sensitive to human disturbance. Restrict entry at colonies with excessive human disturbance. In some cases, posting signs to discourage visitors may be effective. However, signs may also draw attention to colony sites and may be ineffective when enforcement is not possible. Efforts to educate the public may be the most reasonable method of reducing disturbance.
6) Maintain a minimum disturbance-free buffer zone of 330 to 590 feet (100 to 180 m) at breeding colonies.
7) Maintain vegetation buffer zones to block siltation, pesticide, and fertilizer runoff into aquatic habitat. This is particularly important where American White Pelican colonies are adjacent to agricultural land, and vulnerable to contamination from agricultural runoff.
8) Consider building and maintaining artificial islands in areas where a lack of suitable nesting habitat is limiting American White Pelican reproduction. Construct islands of soil or dredged materials, at least ¼ acre (0.1 ha) in size. Islands should be flat and situated well offshore for protection from mammalian predators and human disturbance.
Primary
Habitat Type: Montane Riparian
SPECIES & STATUS |
VEGETATION COMPOSITION |
VEGETATION STRUCTURE |
ABIOTIC FACTORS |
LANDSCAPE FACTORS |
SPECIAL FACTORS |
|
Harlequin
Duck (HARD) Histrionicus histrionicus Level
II M,
P |
|
~Dense
streamside shrubs ~Overhanging
vegetation |
~Remote
mountain streams ~Good
water quality |
~Sections
of stream with low gradient (<5%), braided channels, sections with swift
currents ~Mid
and late succession |
~Strong
fidelity to breeding streams and natal areas ~Very
sensitive to human disturbance in breeding territories ~Requires
abundant aquatic insects ~Arrives
in WY late April; by mid July most males and nonbreeding females depart;
females with young depart from mid August to late September ~Winters
in coastal |
Found
only in the northwestern corner of
1) Breeding Bird Survey (BBS) data from 1968 through 2002
are inadequate to determine population trends for the Harlequin Duck in
1) Maintain water quality in high elevation mountain habitats by eliminating or limiting habitat changes that are detrimental to Harlequin Ducks, such as tie hack logging, sediment loading, and development.
1) In areas where Harlequin Ducks nest, ensure that old growth occurs in and around premier streams, and that recreation, grazing, forest management, and logging do not impact preferred nesting habitat.
2) In areas where Harlequin Ducks nest, maintain high water quality and stream stretches with high densities of invertebrates.
3) Avoid clearing debris from high elevation mountain streams to ensure Harlequin Duck nesting and feeding habitat is present.
4) Avoid trail construction and maintenance, other management activities, or intense recreation along known Harlequin Duck breeding streams during the first 7 to 10 days after hatching, as they are especially vulnerable to disturbance during this time. If necessary in areas of intense activity, close stream sections where Harlequin Ducks are known to breed while the chicks are flightless (June to early August).
Primary Habitat Type: Low
Elevation Conifer
|
SPECIES & STATUS |
VEGETATION COMPOSITION |
VEGETATION STRUCTURE |
ABIOTIC FACTORS |
LANDSCAPE FACTORS |
SPECIAL FACTORS |
|
Merlin (MERL) Falco columbarius Level
II M |
~Ponderosa
pine ~Douglas-fir ~Open
woodlands close to grasslands or shrub-steppe |
~Trees
spaced well apart whose lower 8 to 10 feet are bare of branches ~Open
understory |
~Sometimes
in cities and towns |