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Bird Habitat Conservation Toolkit

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Clark’s Nutcracker caches pine seeds for eating later, but they don’t relocate every last one. The nationally Endangered Whitebark Pine relies on this species’ forgotten caches for seed dispersal.

Clark's Nutcracker

(Nucifraga columbiana)
Overview
status
AlbertaSensitive
British ColumbiaYellow
SaskatchewanAbsent
Primary Habitat
Semi-open/Mountains/Conifer
Nest Type
Canopy (Conifer)
Territory Size
100–300 ha or larger
Nest Reuse
Unknown
Breeding Window
Jan
Feb
Feb
Mar
Apr
May
Jun
Jul
Aug
Aug
Sep
Oct
Nov
Dec
Peak: Mid-April to early July
Stand-Level
Selective cutting followed by prescribed burn to promote open whitebark/limber pine stands
Landscape-Level
Whitebark pine stands >10 ha with >1,000 cones/ha are essential habitat

Habitat Ecology

  • Clark’s Nutcracker occupies semi-open montane and subalpine coniferous forests dominated by ponderosa pine, Douglas fir, limber pine, and/or whitebark pine.1
  • It is a resident species that is found mainly in subalpine forests in the spring and summer, moving down to montane forests in the late autumn, although these movements are not consistent among all populations.1,2
  • Clark’s Nutcracker is rarely found at altitudes higher than 2,600 m.1
  • This species breeds as early as January, with peak breeding from early February to late May. This means that standard avoidance techniques may be ineffective for reducing incidental take.1

Response to Forest Management

  • Clark’s Nutcracker is highly threatened by tree mortality and reduced cone production resulting from mountain pine beetle outbreaks and whitebark pine blister rust.3
  • Fire suppression in the Rocky Mountains has made whitebark pine more vulnerable to these threats.1
  • Recent clearcuts may be used for seed caching, as well as recent openings caused by burns.4

Stand-level Recommendations

  • This species requires ≥10 ha whitebark pine stands with an average cone density of ≥1,000 cones/ha.5 The following actions are recommended where these stands, or stands nearly meeting these conditions, are identified:
  • In collaboration with provincial land managers, prescribed burning at a location within 10 km of the stand can create habitat for caching.5
  • Planting of rust-resistant whitebark pine seedlings in stands that approach but do not meet this threshold.5
  • Thinning treatments targeting non-whitebark pine species, followed by prescribed burning, may create caching habitats. The effectiveness of this approach has been mixed and it should be undertaken with caution.6,7

Landscape-level Recommendations

  • Maintenance or restoration of healthy populations of limber pine and whitebark pine are considered essential to maintaining Clark’s Nutcracker populations.8
  • Whitebark pine restoration is recommended for locations adjacent to habitat mosaics that include Douglas fir, an alternative food source which may attract Clark’s Nutcracker.9

Knowledge Gaps

  • Studies have mainly focused on Clark’s Nutcracker responses to whitebark pine restoration treatments, while responses to conventional harvests are unclear.
  • Sensitivity to human disturbance is unknown during their winter nesting period.1 This knowledge gap has implications for avoiding incidental take and the unknown effectiveness of nest buffering.

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