Slender-billed white-breasted nuthatch (Sitta carolinensis aculeata)

A white, blue and black plumed white-breasted nuthatch perched on a pine tree trunk
A white-breasted nuthatch forages in a ponderosa pine forest.
Category: Birds
State status: Candidate
Vulnerability to climate change (More details)

Low-
Moderate

If you see this species, please share your observation using the WDFW wildlife reporting tool or email us at  wildlife.data@dfw.wa.gov. Be sure to include a photo of the species for verification and location (latitude/longitude coordinates) of your observation. 

Description and Range

Geographic range

White-breasted nuthatches are a common small passerine of deciduous forest in much of North America. The slender-billed subspecies is restricted to parts of western Washington, western Oregon, California, and extreme northern Baja (AOU 1957). It has a slimmer bill, is smaller, and has buffier underparts than the much more common subspecies (S. c. tenuissima) present in eastern Washington. Genetic analyses indicate that slender-billed white-breasted nuthatches are genetically distinct from other populations in North America, but also demonstrate significant genetic differentiation among populations within this subspecies (Spellman and Klicka 2007).

White-breasted nuthatches, including the slender-billed subspecies, are weak cavity excavators and therefore most often use naturally occurring cavities in living trees for roosting and nesting. Cavities made by woodpeckers and nest boxes are also occasionally occupied (Wilson et al. 1991, Viste-Sparkman 2006). Individuals use multiple cavities during the year (Gumtow-Farrior 1991).

In Washington and Oregon, slender-billed whitebreasted nuthatches are commonly associated with Oregon white oak (Chappell 2005, Hagar 2006), as well as black cottonwood and Oregon ash (R. Hill, pers. comm.). Nuthatch densities are greater in areas with higher numbers of large trees, which provide more surface area for foraging and have more natural cavities for nesting and roosting (Hagar and Stern 2001, Viste-Sparkman 2006). Large open-grown oaks in woodlands with sparse understories are particularly important as habitat because these trees have more cavities and foraging substrate than oaks grown in densely vegetated habitats. Birds are therefore more abundant in smaller (25 ha, 62 ac) patches (Viste-Sparkman 2006). In Oregon’s Willamette Valley, oaks with nests average 70 cm (27.5 in) in diameter (Viste-Sparkman 2006). Pairs establish territories of about 10-15 ha (25-37 ac) and occupy the same territories year-round (Pravosudov and Grubb 1993, Hagar 2006).

Foraging typically occurs on the trunk and larger limbs of trees. Fissured bark, which occurs more on larger trees, supports a greater abundance and diversity of arthropods than smooth bark. In the Willamette Valley, weevils and earwigs are important parts of the diet during breeding and post-breeding periods, with variation in the diet decreasing in winter (Anderson 1976). Slenderbilled white-breasted nuthatches also often feed on acorns during winter, and large oaks produce more acorns (Peter and Harrington 2002).

Distribution and population trends

Slender-billed white-breasted nuthatches remain somewhat common and widespread in lowland areas of Clark County, with numbers appearing to be highest in the vicinity of Ridgefield National Wildlife Refuge (eBird reports; Chappell 2005; R. Hill, pers. comm.). Population trend in the county is unknown. Birds in this population make extensive use of ashes, cottonwoods, and oaks. The population is probably an extension of the broader population ranging through the Williamette Valley north to Sauvie Island in Oregon. Birds occurred in the area between Woodland and Kalama in Cowlitz County from 1985-1995, but breeding season records have become rare there and no observations of nesting have been made in recent years (Altman 2011).

The subspecies was reportedly once most abundant in the oak/prairie areas of Pierce and Thurston counties (Bowles 1929, Kitchin 1934, Jewett et al. 1953), but did not breed north of Seattle or in the San Juan Islands (Chappell 2005, Altman 2011). The population in South Puget Sound declined greatly by the early 20th century (Dawson and Bowles 1909, Bowles 1929, Kitchin 1934), although birds were still common in south Tacoma and regularly occurred on Joint Base Lewis-McChord in the mid-1960s (Altman 2011). Further decreases took place in Pierce County in the 1980s, when the last nine breeding sites disappeared; the last reported sighting during the breeding season was in 1998 and the subspecies is now considered extirpated in this region (Chappell 2005, Altman 2011).

Factors affecting populations

Oregon white oak-prairie habitats were once far more widespread in South Puget Sound, but have experienced dramatic declines and are among the most threatened habitats in the Pacific Northwest (Hanna and Dunn 1997, ABC 2006). Factors contributing to their loss or degradation include urban, residential, and rural development; harvest of oak trees; conversion to agriculture; fire suppression and associated encroachment by conifers; conversion of oak woodland and forest to conifer stands for timber production; and lack of oak recruitment (Hanna and Dunn 1997, Altman 2011). The decrease of oak habitats has likely been the main cause of the decline and extirpation of slender-billed white-breasted nuthatches from the South Puget Sound lowlands (Altman 2011). Other contributing factors may include scarcity of nesting cavities, competition from starlings for nest sites, insufficient oak mast to support overwintering populations, genetic drift due to small isolated populations, and unknown disease or natural disturbance (Chappell 2005).

Climate vulnerability

Sensitivity to climate change

Low-
Moderate

This species likely has low physiological sensitivity to climate change, but little information is available. As a near-obligate of oak woodlands, this species is likely more sensitive to changes in mature oak woodland nesting and foraging habitat as a result of climate change. Snags and large, mature trees provide superior forage grounds and more space for nesting cavities, which are created by woodpeckers. Increased fire frequencies may help restore more open, mature oak habitat by reducing oak density and conifer encroachment. Fire and wind events may also create important edge openings preferred by this species. Temperature increases and precipitation changes may affect insect prey availability. Any reductions in oak habitat in response to climate change would likely negatively affect this species, for although they will nest in mixed deciduous-coniferous woodlands, past oak woodland loss has been associated with species extirpation from portions of Washington State (e.g., Puget Sound).

Confidence: Low

Exposure to climate change

Low-
Moderate

  • Increased temperatures
  • Changes in precipitation
  • Altered fire regimes
Confidence: Moderate

Conservation

This species is identified as a Species of Greatest Conservation Need (SGCN) under the State Wildlife Action Plan (SWAP). SGCN-classified species include both those with and without legal protection status under the Federal or State Endangered Species programs, as well as game species with low populations. The WDFW SWAP is part of a nationwide effort by all 50 states and five U.S. territories to develop conservation action plans for fish, wildlife and their natural habitats—identifying opportunities for species' recovery before they are imperiled and more limited.
This species is identified as a Priority Species under WDFW's Priority Habitat and Species Program. Priority species require protective measures for their survival due to their population status, sensitivity to habitat alteration, and/or recreational, commercial, or tribal importance. The PHS program is the agency's main means of sharing fish and wildlife information with local governments, landowners, and others who use it to protect priority habitats for land use planning.

Conservationists have long been aware of the importance of preserving oak communities and their associated wildlife, including slender-billed white-breasted nuthatches, in the Pacific Northwest. Numerous habitat management and restoration projects have been undertaken (e.g., Hanna and Dunn 1997, Devine and Harrington 2004, Dunwiddie and Bakker 2011), although replacing the large oaks that were present historically will require many decades. WDFW developed Priority Habitat and Species (PHS) management recommendations for oak woodlands (Larsen and Morgan 1998), and many other management plans, recommendations, and landowner guides have been published for this habitat (e.g., Columbia Gorge Audubon Society 1991, Vesely et al. 2004, Harrington and Devine 2006, Altman and Stephens 2012).

Based on the findings of a feasibility assessment (Slater and Altman 2012), a cooperative project was initiated in 2012 by the Ecostudies Institute, American Bird Conservancy, and Joint Base Lewis-McChord to reintroduce a population of slender-billed white-breasted nuthatches into South Puget Sound. The assessment determined that adequate oak woodland existed in the region to support a population of more than 300 birds. This work is planned for 2013 using 4-10 pairs of nuthatches from western Oregon (Slater and Altman 2012).