Mimus graysoni


Taxonomy [top]

Kingdom Phylum Class Order Family

Scientific Name: Mimus graysoni
Species Authority: (Lawrence, 1871)
Common Name(s):
English Socorro Mockingbird, Socorro Thrasher
Mimodes graysoni Sibley and Monroe (1990, 1993)
Mimodes graysoni Stotz et al. (1996)
Mimodes graysoni Collar and Andrew (1988)
Mimodes graysoni Collar et al. (1994)
Mimodes graysoni BirdLife International (2000)
Mimodes graysoni BirdLife International (2004)
Taxonomic Notes: Formerly treated in the monotypic genus Mimodes; transferred to the genus Mimus following AOU (2005).

Assessment Information [top]

Red List Category & Criteria: Critically Endangered B1ab(ii,iii) ver 3.1
Year Published: 2013
Date Assessed: 2013-11-01
Assessor(s): BirdLife International
Reviewer(s): Butchart, S.
Contributor(s): Keitt, B., Martínez-Gómez, J. & Tershy, B.
Facilitator/Compiler(s): Bird, J., Butchart, S., Capper, D., Isherwood, I., Pople, R., Sharpe, C J, Symes, A., Temple, H.
Intensive sheep-grazing and a persistent locust swarm are reducing and degrading habitat for this species. Combined with cat predation, which effectively removes mockingbirds from areas with little or no understorey, declines in its very small population and extremely small range are considered likely. This combination of factors qualifies the species as Critically Endangered.

2012 Critically Endangered

Geographic Range [top]

Range Description: Mimus graysoni is endemic to Socorro in the Revillagigedo Islands, Mexico. It was the most abundant and widespread landbird in 1925, and was still abundant in 1958. By 1978, it had declined dramatically and was feared on the verge of extinction. Subsequent surveys have estimated the population at 50-200 pairs in 1988-1990 (Castellanos and Rodríguez-Estrella 1993, Wehtje et al. 1993, Rodríguez-Estrella et al. 1996) and c.350 individuals in 1993-1994, with the highest densities in the sheep-free dwarf forests of Cerro Evermann (Martínez-Gómez and Curry 1996). Of 170 birds ringed in 1994, 56% were subadults (Martínez-Gómez and Curry 1996), suggesting that productivity is high and the population would be capable of increasing if habitat quality improves across the island (J. E. Martínez-Gómez in litt. 2007).

Range Map: Click here to open the map viewer and explore range.

Population [top]

Population: Martinez-Gomez & Curry 1996 calculated a total population of 353 (287-419) individuals based upon comprehensive ringing data. Visits by the author to the same sites during 2006 & 2007 reported a similar population. The estimate is best applied to the area of the island where ringing took place. This implies that the total population of the island may be larger (J. E. Martinez-Gomez in litt. 2007). This roughly equates to 190-280 mature individuals.
Population Trend: Stable

Habitat and Ecology [top]

Habitat and Ecology: It occurs principally in moist dwarf forest and ravines with a mixture of shrubs and trees at elevations above 600 m (Martínez-Gómez and Curry 1996). Vegetation in these areas is dominated by the trees Ilex socorrensis, Guettarda insularis and Oreopanax xalapensis and the understorey species Triumfetta socorrensis and Eupatorium pacificum (Martínez-Gómez and Curry 1996, Martínez-Gómez et al. 2001). It is very rare at low and mid-elevations (0-500 m), and absent from areas of Croton masonii scrub near sea-level and sheep-damaged habitat in the south-east half of the island (Martínez-Gómez and Curry 1996, Martínez-Gómez et al. 2001), but is common within fig Ficus cotinifolia patches in the north-west of the island (J. E. Martínez-Gómez in litt. 2007). Fig groves may act as regeneration nuclei for the species, supporting birds when a suitable understorey is present (J. E. Martínez-Gómez in litt. 2007). Nesting may occur from November-July with a peak in March-April (Martínez-Gómez and Curry 1995). Three eggs are laid and the incubation period is no more than 15 days (Martínez-Gómez and Curry 1995). Food includes crab remains, small invertebrates and fruit, particularly those of Ilex socorrensis and Bumelia socorrensis (Castellanos and Rodríguez-Estrella 1993, Martínez-Gómez et al. 2001).

Systems: Terrestrial

Threats [top]

Major Threat(s): Sheep had intensively grazed almost one third of the island by 1990 (Castellanos and Rodríguez-Estrella 1993), leaving no suitable nesting or foraging habitat in the south of the island (Martínez-Gómez and Curry 1996). Predation by feral cats was initially thought responsible for the species's decline, but cats were introduced some time after 1972 (Martínez-Gómez et al. 2001), and examinations of cat stomach contents and scats have not provided any substantive evidence (Martínez-Gómez and Curry 1996). However, they are likely to prey upon dispersing individuals that move into areas with little or no understorey (J. E. Martínez-Gómez in litt. 2007). Competition with the immigrant Mimus polyglottos is probably not a factor because Mimus graysoni is much larger, has different habitat preferences and is not outcompeted in undisturbed habitats (Castellanos and Rodríguez-Estrella 1993, Martínez-Gómez and Curry 1996). Since 1994, c.30 ha of forest have been lost owing to a now permanent locust Schistocerca piceifrons swarm on the island which irrupts twice yearly. Its effects are thought to be more severe owing to the degradation of native vegetation by introduced grazing mammals, and the suppression of native bird populations (which typically exert top-down control of insect populations on the island) by introduced cats. Locusts cut leaves, flowers and fruit from trees and thus represent a serious threat to fruit eaters such as Socorro Mockingbird (J. E. Martínez-Gómez in litt. 2007). Potential developments on Socorro including enlargements to the airstrip and the possibility of a new federal prison could destroy breeding habitat and increase the risk of accidental introduction of other invasive species.

Conservation Actions [top]

Conservation Actions: Conservation Actions Underway
The Revillagigedo Islands were declared a Biosphere Reserve in 1994 (Rodríguez-Estrella et al. 1996). There is an ongoing control programme in the region (the Mexican navy has effectively reduced the sheep population to c. 300 heads), and there are plans to eradicate cats and sheep from Socorro (B. Tershy in litt. 1999, B. Tershy and B. Keitt in litt. 1999).

Conservation Actions Proposed
Eradicate cats and sheep from Socorro (Martínez-Gómez and Curry 1996, B. Tershy in litt. 1999, B. Tershy and B. Keitt in litt. 1999). Implement a vegetation and soil restoration plan after sheep have been removed (Martínez-Gómez et al. 2001). Establish a captive-breeding population, and a research monitoring station on Socorro (Rodríguez-Estrella et al. 1996). Monitor the population, especially before and after the proposed eradications.

Citation: BirdLife International 2013. Mimus graysoni. The IUCN Red List of Threatened Species. Version 2015.2. <>. Downloaded on 28 August 2015.
Disclaimer: To make use of this information, please check the <Terms of Use>.
Feedback: If you see any errors or have any questions or suggestions on what is shown on this page, please provide us with feedback so that we can correct or extend the information provided