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Severtzov's Grouse Tetrastes sewerzowi Scientific name definitions

Eduardo de Juana and Guy M. Kirwan
Version: 1.0 — Published March 4, 2020
Text last updated February 22, 2016

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Field Identification

33–40 cm (1); male 279–390 g, female 270–407 g (1). Male mass varies from lowest during breeding season to highest in winter, whereas the reverse is true in females (2). The world’s smallest grouse (1). Very similar to B. bonasia but has less feathered tarsus (3); upperparts more broadly barred black and upper breast more chestnut, with only small white tips to feathers; tail has quite different barred pattern. Female has less obvious red comb  and further differs from male in being overall duller, with black throat largely obscured by whitish fringes to feathers , and buffier underparts with less intense black barring (3). Irides dark brown, bill black, and feet greyish black (3). Juvenile plumage is apparently unknown (3). Race secunda is described as being more rufous than nominate.

Systematics History

Editor's Note: This article requires further editing work to merge existing content into the appropriate Subspecies sections. Please bear with us while this update takes place.

Formerly placed in genus Tetrastes, but genetic evidence clearly places both present species and closely related B. bonasia in Bonasa together with North American B. umbellus (4), despite some behavioural differences between the American and the two Eurasian species (5). Geographical variation slight. S race secunda slightly more rufous, but this is perhaps no more than clinal variation (3). Two subspecies tentatively recognized.

Subspecies

Monotypic.

Distribution

Mountains of C China, from C Gansu and S Qinghai to E Tibet, NW Yunnan and N Sichuan.

Habitat

Birch and coniferous mountain forests, generally above 2400 m, and as high as 4300 m in Tibet (6); the elevation occupied increases with decreasing latitude, e.g. breeds at 2350–3000 m in Qilian Mts of NW Gansu, but at 3530–3820 m in NW Yunnan. Records as low as 1000 m are probably doubtful (6). In places, may reach treeline and during summer even alpine belt, in areas of rhododendron. In Gansu, main habitat types centred on dragon spruce (Picea crassifolia or P. asperata) and Abies fargesii (1), sometimes with 60–90% cover of moss (Abietinella, Bryum) on forest floor; other typical plants include birch (Betula), willow (Salix) and barberry (Berberis); grassland and alpine shrubs generally avoided. Females with broods chose sites with significantly less canopy cover, greater willow cover and greater herb height, using a variety of vegetation types at different stages of chick development (7).

Movement

Apparently sedentary. Mean territory size of paired male in spring is c. 2·1 ha (range in one study 1·8–3·2 ha) (8), and of unpaired male c. 2·7 ha (9). Radio-tracking data reveal that home ranges of males in winter range from 6 ± 1·6 ha (n = 9) to 16 ± 2·6 ha (n = 10); most females and all yearlings form mixed-sex flocks at this season (between mid Oct and mid Mar) (3), whereas adult males either remain on breeding territory, move to winter flocking area (where groups typically number 4–5 to 13–14 individuals) (10), or wander between spring territory and wintering area (10, 11), but females can also briefly form territories in autumn (12). Those males that join flocks in winter leave these earlier in spring (2).

Diet and Foraging

In Gansu, mainly flower and leaf buds of willow and birch in early spring, moving onto flower buds and leaves of the same species by May; in Jun–Jul, seeds and inflorescences of Polygonum dominate, while for brief period in autumn mountain ash (Sorbus) berries are clearly preferred (13); between Jan and Mar, sea buckthorn (Hippophae rhamnoides) is important (10), but willow buds and twigs (83% of foraging observations) of six main species are still the most important constituent, of which Kangding willow (Salix paraplesia) is the most preferred species and Sichuan willow (S. hylonoma) the least (14). In late Apr–May willows are the primary food of males (> 98% wet biomass), while spruce (Picea aspera) seeds and willow are primary food of females, which also eat frequently invertebrates (mainly ants) and forbs (possibly to meet the nutrient demands of egg formation) (15). Forages on ground or in trees.

Sounds and Vocal Behavior

Territorial displays are given in both spring and autumn (2). Males perform a wingbeat display, with variable flutter-jumps (the wings making a “pu pu pu pu” sound) (3) from the ground reaching up to 1 m high and 2–4 m wide, sometimes also from a tree to the ground and vice versa, especially immediately after leaving the the roost until c. 08:00 hours (16); this display serves to advertise territory and attract females, but perhaps also as a warning signal (8). Noisy territorial flights in the crowns of trees are rare (16). The low-frequency sounds generated by the wings produce an impressive concert, especially if 3–4 conflicting males are in close proximity (16). Male–male aggression displays include hoarse “en er en er en...” sounds comprising separate trill and squeak phases comprising three and 4–7 elements, respectively, sometimes with a cackling sound given after the trill (13), while females utter a “ze ze ze-dackdack” in company of chicks to alert them to potential predators (3), but four different types of alarm calls have been identified (17), including a longer “tetetetete... ” uttered by a female during an encounter with males (13).

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Breeding

Laying from end May to mid Jun (3). Monogamous; although polyandry is occasionally suspected (8, 18), only available evidence suggests strong pair-bonds (2); male territories established in late winter (3), but pairs form in late Mar (18), with copulation observed from second week of May (16). As many as 44% of males did not mate in one study (19). Nest scrape (c. 43 mm by 30·5 mm) (3) at base of tree, in tree stump or on rocky ledge; constructed of grass, sometimes lined with pine needles and partly edged with moss; of 103 nests found in one study, 56% were at base of deciduous trees, mainly willows (Salix spp.) and birches (Betula utilis), and 40% at base of conifers, typically sited on N- or E-facing slopes and 88% of nests were on slopes < 30º, while females often nested within c. 150 m of the previous year’s site (20). Will occasionally re-nest if first clutch is lost (19). Clutch 5–8 (mean 6·19 in one study) (1) pale yellow (1) or yellowish-brown (3) eggs with diffuse chestnut markings (3), size 40–43·5 mm × 30·8–31·5 mm (1), mean mass 20·5 g, laid every 48 hours (2); incubation 25 days (in captivity) by female alone (3), but 27–29 days in wild (2); downy chicks have head markings more apparent than in other Bonasa, tended by female alone, remain with adult for 2–3 months and then disperse up to 5 km (2); mean 3·62 young/year per female fledged in one study (19); nest loss is 37%, of which 10–29% is caused by egg collecting by local people (19), but hatching success in one study was 93% (2). Mortality suspected to be c. 68% within first year of life, declining to 34–39% per annum thereafter (9), although one study reported that only 17% of chicks survive to 13 weeks old (19). Potential mammalian predators of eggs and/or adults include dhole (Cuon alpinus), raccoon dog (Nycterentes procyonoides), stone marten (Martes foina), Siberian weasel (M. sibirica), sand badger (Arctomyx collaris), Pallas’ cat (Felis manul), leopard cat (F. bengalensis) and Eurasian lynx (Lynx lynx), while among birds various corvids, owls and diurnal raptors inflict even more severe losses among adults (19). Males thought to achieve sexual maturity when two years old, but females a year earlier (9). Overall population is thought to be skewed towards males, 64% versus 36% in females, at least locally (9). Maximum recorded longevity just over five years (19).

Not globally threatened. Currently considered Near Threatened. Listed as endangered in Chinese Red Data book. Total range speculated to be c. 394,000 km² and population c. 10,000 birds (21); range recently (1997) (6) discovered to be more extensive than previously thought in W, and species may yet prove to be widespread in suitable habitat in SE Tibet. Very few data available, although knowledge of the species has noticeably advanced in recent decades. Known from at least 18 protected areas across range, of which eight are in Sichuan, six Gansu and two each in Qinghai and Yunnan (6). Common in suitable forest, e.g. density of 15 occupied territories/km² in Lianhuashan Natural Reserve (S Gansu) (16) and 4–6 pairs/ha at Zhongdian (Yunnan) but just 0·27–2 birds/km² at Baihe Natural Reserve (Sichuan) (6); species has disappeared from E Qinghai and C Gansu, due to deforestation, and is also experiencing intensive habitat loss in SW Gansu; climate change, which is speculated to lead to increasing aridity within the species’ range, is also cause for concern (22). Can probably persist in selectively logged forest, albeit at obviously lower densities (6), with habitat fragmentation (as well as degradation and outright loss) an additional risk (2, 23), as species prefers patches larger than 40 ha and suitable but unoccupied habitat fragments isolated by > 2 km are apparently inaccessible to the species (24). Significant predation of eggs by Large-billed Crows (Corvus macrorhynchos), accounting for failure of 50% of nests located during recent study, but egg-collecting by local people, even within protected areas is also an important threat (9). Illegal hunting also occurs (9), with some people admitting to shooting 60–80 birds per year (21).

Distribution of the Severtzov's Grouse - Range Map
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  • Year-round
  • Migration
  • Breeding
  • Non-Breeding
Distribution of the Severtzov's Grouse

Recommended Citation

de Juana, E. and G. M. Kirwan (2020). Severtzov's Grouse (Tetrastes sewerzowi), version 1.0. In Birds of the World (J. del Hoyo, A. Elliott, J. Sargatal, D. A. Christie, and E. de Juana, Editors). Cornell Lab of Ornithology, Ithaca, NY, USA. https://doi.org/10.2173/bow.sevgro1.01
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