Species: Amphispiza bilineata

Black-throated Sparrow
Species
    Kingdom
    Animalia
    Phylum
    Craniata
    Class

    Aves

    Order

    Passeriformes

    Family

    Emberizidae

    Genus

    Amphispiza

    Classification
    Other Global Common Names
    Bruant à gorge noire - Zacatonero Garganta Negra
    Informal Taxonomy
    Animals, Vertebrates - Birds - Perching Birds
    Formal Taxonomy
    Animalia - Craniata - Aves - Passeriformes - Emberizidae - Amphispiza
    Short General Description
    A small bird (sparrow).
    Migration
    true - true - true - Migrant in northern parts of range. In northern Arizona, departs mid-August, returns late March; in southern Arizona, arrives in early March (Phillips et al. 1964).
    Non-migrant
    true
    Locally Migrant
    true
    Food Comments
    Feeds on seeds, insects, spiders, and green grass shoots. In winter, feeds primarily on seeds; in breeding season on insects. Forages on the ground; ingests gravel while ground feeding. Will also glean insects from shrubs and herbs and will hawk aerial insects. Young are fed insects, especially grasshoppers. During some seasons this species can obtain daily water requirement from insects and green vegetation; in dry season, when seeds are main food source, will drink regularly at water holes (Bent 1968).
    Reproduction Comments
    Clutch size two to four, usually three to four. Duration of incubation and nestling periods are unknown. Nestlings are altricial and downy. Nesting occurs from February through mid-August, depending on region; most records between April and June; time of breeding can vary greatly from year to year depending on rainfall and food abundance (George 1987b, Ehrlich et al. 1988, Rising 1996). Will raise two broods (Ehrlich et al. 1988). In a creosote bush community in Nevada, this sparrow was found to be one of only two bird species that bred during dry years (Hill 1980). One record of egg-dumping of a Sage Sparrow (AMPHISPIZA BELLI) egg in a black-throated sparrow nest, in an area where territories overlapped (Gustafson 1975). <br><br>During times of hot months with limited water, can apparently suppress normal adrenocortical response to heat stress, which may allow breeding to continue despite extreme temperatures; the response is then reactivated in winter months (Wingfield et al. 1992).
    Ecology Comments
    Relative abundances recorded on BBS routes are high, ranging from and average 11.76 to 23.42 birds per 25-mile survey route. Density of 7 per 40 hectares has been reported for desert scrub creosote-burrobush habitat in California (Kubik and Remsen 1977); in another study, 3.9 per 40 hectares (Bureau of Land Management, no date). In southern Utah, breeding densities ranged from 4.3 to 9.6 pairs per 40 hectares (Medin 1986). In a creosote bush community in Nevada, occurred in densities of 43-61 pairs per 100 hectares (Hill 1980). In Baja California, average density of individuals was significantly higher on island study sites (16 individuals per 10 hectares) than on mainland sites (7.0 per 10 hectares; George 1987a). In New Mexico creosote bush scrub habitat, territory sizes were estimated at 120-150 meters in diameter (Heckenlively 1967). <br><br>Chases are common among males when territories are being established (Rising 1996). Visibility in habitat can be limited, and singing both elicits defense behavior and is apparently the most frequent response for territorial defense (Heckenlively 1967). <br><br>During nonbreeding season, found in small foraging flocks and often in mixed-species flocks that may include sage sparrows (AMPHISPIZA BELLI), Brewer's sparrows (SPIZELLA BREWERI), white-crowned sparrows (ZONOTRICHIA LEUCOPHRYS), vesper sparrows (POOECETES GRAMINEUS), cactus wrens (CAMPYLORHYNCHUS BRUNNEICAPILLUS) or verdins (AURIPARUS FLAVICEPS; Ehrlich et al. 1988, Rising 1996). <br><br>In a study conducted between early March and late May in southern Arizona, birds foraged on ground more than 90 percent of the time (Parker 1986). Seed foraging is apparently facilitated by the presence of rodents and ants, possibly through the creation of runways and bare areas which the sparrows use for visual foraging. Sparrow abundance declined over the long-term with the removal of rodents and ants (Thompson et al. 1991).
    Length
    14
    Weight
    14
    NatureServe Global Status Rank
    G5
    Global Status Last Reviewed
    1996-12-04
    Global Status Last Changed
    1996-12-04
    Other Status

    LC - Least concern

    Conservation Status Map
    <img src="http://www.natureserve.org/explorer/servlet/GetMapGif?US.AZ=S5&US.CA=SNR&US.CO=S3&US.ID=S2&US.NN=S5&US.NV=S5&US.NM=S5&US.OK=S1&US.OR=S3&US.TX=S4&US.UT=S5&US.WA=S1&US.WY=__" alt="Conservation Status Map" style="width: 475px; height: auto;" />
    Global Range
    BREEDING: eastern Washington, southern Oregon, northeastern California, southwestern Idaho, southwestern Wyoming, southeastern Colorado, northwestern Oklahoma, and north-central Texas south to southern Baja California, the northern Jalisco, Guanajuato, Queretaro, Hidalgo, Tamaulipas, and southern Texas (Godfrey 1966, AOU 1998). NON-BREEDING: from southeastern California, southern Nevada, southeastern Arizona, southern New Mexico, and southern Texas south through breeding range (Godfrey 1966, AOU 1998).
    ELEMENT_GLOBAL.2.101363