The Oregon vesper sparrow is a subspecies of vesper sparrow. It has a restricted breeding range that includes southwestern British Columbia, western Washington, western Oregon, and northwestern California. Oregon vesper sparrows are present in western Washington primarily from early April through late September, and they migrate to winter in central and southern California. Due to loss and degradation of habitat this subspecies is now in danger of extirpation in Washington.
Description and Range
Vesper sparrows are a large sparrow (6 inches in length) with pale brown-streaked plumage, white outer tail feathers, rufous lesser wing coverts, and a white eye-ring.
Ecology and life history
Oregon vesper sparrows breed in dry grassland and open habitats (examples: lowland prairies, some airfields) in western Washington. Breeding territories at Joint Base Lewis-McChord were in areas of high-quality prairie supporting intact Idaho fescue near prairie edges. Prairie size appears to be an important factor in site selection, with only large prairies occupied now. In western Oregon, they use areas with extensive grass and weed cover, or in lightly grazed pastures with scattered shrubs and grass heights of less than one to two feet tall.
Vesper sparrows feed on a wide variety of insects during the breeding season supplemented with seeds during migration and winter.
They build a bulky, loose, cup-like nest of grasses and rootlets on the ground in a small depression, often near the base of a grass clump, weed, or shrub. The female typically lays three to five eggs in mid-May and incubates them for 11 to 13 days. The young fledge in 7 to 12 days, and pairs commonly raise two broods per season. Vesper sparrows exhibit relatively high annual site fidelity to nesting areas and defend small territories during the breeding season.
Vesper sparrows are often seen in loose flocks before fall migration.
Vesper sparrows occupy open habitats (grassland, shrub-steppe, and agriculture) across much of central and southern North America. The Oregon vesper sparrow is the rarest of four recognized subspecies. It has a restricted breeding range that includes southwestern British Columbia, western Washington, western Oregon, and northwestern California. It is migratory and overwinters rom central California west of the Sierra Nevada Mountains to northwestern Baja California, Mexico.
Historical accounts suggest the Oregon vesper sparrow was locally uncommon to abundant in the disjunct distribution of grassland and savannah habitat in western Washington. It has experienced range-wide population declines and range contractions, and many local extirpations. In Washington, this includes 20th century extirpations from Vashon Island of the north Puget lowlands, and the Dungeness area of the Olympic Peninsula; and extirpation from San Juan Island appears likely. It is now mainly limited in Washington to remnant prairies and grasslands in Pierce and Thurston Counties, with smaller numbers on islands in the lower Columbia River and grasslands on San Juan Island; a few may still breed in eastern Clallam County and near Shelton (Mason County).
Approximately 90% of the population occurs in the south Puget lowlands, predominantly on Joint Base Lewis-McChord. The current range-wide population estimate is less than 3,000 birds with approximately 300 of those occurring in Washington.
For a map reflecting this species' conservation status and other species' information, check out NatureServe Explorer and the International Union for Conservation of Nature Redlist.
Sensitivity to climate change
Oregon vesper sparrow sensitivity is largely driven by their dependence on open habitats, seeds, and insects. They nest and forage on the ground in open habitats (e.g., grasslands or shrublands with patchy vegetation and some bare ground); increasing fire frequency, temperatures, and more variable precipitation may decrease habitat availability, quality and connectivity and/or alter foraging opportunities. They may have some physiological sensitivity; for example, low temperatures can undermine nestling growth by increasing thermoregulatory costs and/or decreasing insect prey availability.
Exposure to climate change
- Temperature changes (increase or decrease)
- Changes in precipitation
- Altered fire regimes
Conservation Threats and Actions Needed
- Invasive and other problematic species and genes
- Threat: Invasive Scot’s broom and native conifer forest succession (due to alteration of prairie fire regime).
- Action: Restore and manage degraded habitat at prairies; use prescribed fire where possible; coordinate with airport vegetation management.
- Threat: Increased predation pressure from encroaching urbanization (domestic and feral cats).
- Action: Assess impacts of predation by cats, and assess need for, and approach to, effectively address this risk factor.
- Fish and wildlife habitat loss or degradation.
- Threat: Conservation to agriculture and development. Habitat loss isolates remaining populations.
- Action: Use land acquisitions, conservation easements and landowner agreements to protect habitat.
- War, civil unrest and military exercises
- Threat: Military training exercises disturb nesting and degrades habitat
- Action: Work with Joint Base Lewis-McChord to develop management plan for known breeding habitat.
- Outreach and education
- Threat: Recreational use of prairies; vegetation management (example: mowing airports).
- Action: Public outreach/education and coordination.
- Agriculture and aquaculture side effects
- Threat: Potential herbicide and pesticide effects.
- Action: Education and outreach.
See the Climate vulnerability section above for information about the threats posed by climate change to this species.