Bird abundance and diversity nest on beaver lodge |left Beavers help waterfowl by creating increased areas of water, and in northerly latitudes, they thaw areas of open water, allowing an earlier nesting season. In a study of Wyoming streams and rivers, watercourses with beavers had 75-fold more ducks than those without.
Trumpeter swans (
Cygnus buccinator) and
Canada geese (
Branta canadensis) often depend on beaver lodges as nesting sites. Canada's small trumpeter swan population was observed not to nest on large lakes, preferring instead to nest on the smaller lakes and ponds associated with beaver activity. Beavers may benefit birds frequenting their ponds in several additional ways. Removal of some pondside trees by beavers increases the density and height of the grass–forb–shrub layer, which enhances waterfowl nesting cover adjacent to ponds.
Coppicing of waterside willows and cottonwoods by beavers leads to dense shoot production which provides important cover for birds and the insects on which they feed. Widening of the riparian terrace alongside streams is associated with beaver dams and has been shown to increase riparian bird abundance and diversity, an impact that may be especially important in semiarid climates. As trees are drowned by rising beaver impoundments, they become ideal nesting sites for woodpeckers, which carve cavities that attract many other bird species, including
flycatchers (
Empidonax spp.),
tree swallows (
Tachycineta bicolor),
tits (Paridae spp.),
wood ducks (
Aix sponsa),
goldeneyes (
Bucephala spp.),
mergansers (
Mergus spp.),
owls (Tytonidae, Strigidae) and
American kestrels (
Falco sparverius). By perennializing streams in arid deserts, beavers can create habitat which increases abundance and diversity of riparian-dependent species. For example, such as the upper
San Pedro River in southeastern
Arizona, reintroduced beavers have created a willow and pool habitat which has extended the range of the endangered
Southwestern willow flycatcher (
Empidonax trailii extimus) with the southernmost verifiable nest recorded in 2005.
Bats Beaver modifications to streams in Poland have been associated with increased bat activity. While overall bat activity was increased,
Myotis bat species, particularly
Myotis daubentonii, activity may be hampered in locations where beaver ponds allow for increased presence of
duckweed.
Trout and salmon (
Oncorhynchus nerka) jumping beaver dam |right Beaver ponds have been shown to have a beneficial effect on trout and salmon populations. Many authors believe that the decline of salmonid fishes is related to the decline in beaver populations. Research in the
Stillaguamish River basin in
Washington found that extensive loss of beaver ponds resulted in an 89% reduction in
coho salmon (
Oncorhynchus kisutch) smolt summer production and an almost equally detrimental 86% reduction in critical winter habitat
carrying capacity. This study also found that beaver ponds increased smolt salmon production 80 times more than the placement of large woody debris. Beaver-impounded tidal pools on the Pacific Northwest's
Elwha River delta support three times as many juvenile
Chinook salmon (
Oncorhynchus tshawytscha) as pools without beaver. The presence of beaver dams has also been shown to increase either the number of fish, their size, or both, in a study of
brook trout (
Salvelinus fontinalis),
rainbow trout (
Oncorhynchus mykiss) and
brown trout (
Salmo trutta) in
Sagehen Creek, which flows into the
Little Truckee River at an altitude of in the northern
Sierra Nevada. These findings are consistent with a study of small streams in
Sweden, that found that brown trout were larger in beaver ponds compared with those in
riffle sections, and that beaver ponds provide habitat for larger trout in small streams during periods of drought. Similarly, brook trout, coho salmon, and
sockeye salmon (
Oncorhynchus nerka) were significantly larger in beaver ponds than those in unimpounded stream sections in
Colorado and
Alaska. In a recent study on a headwater Appalachian stream, brook trout were also larger in beaver ponds. Most beaver dams do not pose barriers to trout and salmon migration, although they may be restricted seasonally during periods of low stream flows. In a meta-review of studies claiming that beaver dams act as fish passage barriers, Kemp et al. found that 78% of these claims were not supported by any data. Rainbow, brown, and brook trout have been shown to cross as many as 14 consecutive beaver dams. In Oregon coastal streams, beaver dams are ephemeral and almost all wash out in high winter flows only to be rebuilt every summer. Migration of adult Atlantic salmon (
Salmo salar) may be limited by beaver dams, but the presence of juveniles upstream from the dams suggests that the dams are penetrated by
parr. Downstream migration of Atlantic salmon smolts was similarly unaffected by beaver dams, even in periods of low flows. The importance of winter habitat to salmonids afforded by beaver ponds may be especially important in streams without deep pools or where ice cover makes contact with the bottom of shallow streams. Enos Mills wrote in 1913, "One dry winter the stream ... ran low and froze to the bottom, and the only trout in it that survived were those in the deep holes of beaver ponds."
Cutthroat trout and
bull trout were noted to overwinter in Montana beaver ponds, brook trout congregated in winter in New Brunswick and Wyoming beaver ponds, and coho salmon in Oregon beaver ponds. By creating additional channel network complexity, including ponds and marshes laterally separated from the main channel, beavers may play a role in the creation and maintenance of fish biodiversity. In off-mainstem channels restored by beaver on the middle section of Utah's
Provo River, native fish species persist even when they have been extirpated in the mainstem channel by competition from introduced non-native fish. Efforts to restore salmonid habitat in the western United States have focused primarily on establishing
large woody debris in streams to slow flows and create pools for young salmonids. Research in Washington found that the average summer smolt production per beaver dam ranges from 527 to 1,174 fish, whereas the summer smolt production from a pool formed by instream large woody debris is about 6–15 individuals, suggesting that re-establishment of beaver populations would be 80 times more effective.
Amphibians A study of mid-elevation ( - ) beaver-dammed vs. undammed
lentic streams in
Washington's southern
Cascades found that prevalence of slow-developing amphibian populations was 2.7 times higher in the former, because beaver ponds were deeper with longer
hydroperiods. Specifically, slow developing
northern red-legged frogs (
Rana aurora) and
northwestern salamanders (
Ambystoma gracile) were found almost exclusively in beaver-dammed locations, suggesting that these amphibians depend on beaver-engineered microhabitats. In the arid
Great Basin of the western and northwestern United States, establishment of beaver ponds has been used as a successful management strategy to accelerate population growth of
Columbia spotted frog (
Rana luteiventris), which also depend on ponds with longer hydroperiods. In a report from
Contra Costa County, California, both beaver dams and burrows associated with bank-lodges were found to provide refuge microhabitat for federally listed
threatened California red-legged frog (
Rana draytonii). Beaver-dammed ponds were also found to provide breeding habitat for R. draytonii adults and rearing habitat for their tadpoles. The report recommended that beaver "be treated as critical to the survival" of California red-legged frogs. Beaver-engineered wetlands in the
Boreal Foothills of west-central
Alberta were also found to play a pre-eminent role in establishment of
anuran species including the
boreal chorus frog (
Pseudacris maculata), North American
wood frog (
Rana sylvatica) and
western toad (
Anaxyrus boreas). In northern
New York,
mink frogs (
Rana septentrionalis) were more abundant in larger ponds associated with beaver in the
Adirondack Mountains, possibly because the colder, deeper water associated with large beaver ponds buffers this heat-intolerant species.
Insects The fallen trees and stripped bark produced by beaver activity provides popular sites for oviposition of the virilis group of
Drosophila, including the fruit fly
Drosophila montana. Capture of these species of Drosophila for research is significantly more successful near beaver residences. The preference of beavers for birch, willow, and alder corresponds with oviposition site preferences of the Drosophila virilis species group, leading to commensalism between beavers and these species. ==Effects on riparian trees and vegetation==