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Herpsilochmus pectoralis 

Scope: Global
Language: English
Status_ne_offStatus_dd_offStatus_lc_offStatus_nt_offStatus_vu_onStatus_en_offStatus_cr_offStatus_ew_offStatus_ex_off

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Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Aves Passeriformes Thamnophilidae

Scientific Name: Herpsilochmus pectoralis Sclater, 1857
Common Name(s):
English Pectoral Antwren
Taxonomic Source(s): SACC. 2005 and updates. A classification of the bird species of South America. Available at: #http://www.museum.lsu.edu/~Remsen/SACCBaseline.htm#.
Identification information: 11.5 cm. Long-tailed, well-marked antwren. Male has black crown, white supercilium and black postocular eye-stripe. Grey nape and mantle with black-and-white streaking on latter. Black wings with large white covert tips forming two wing-bars. White spotting on shoulders and fringing to flight feathers. Black tail, boldly tipped white. White underparts with black pectoral crescent. Female has olive upperparts with rufous crown. White tips to uppertail-coverts. Uniform dull buff underparts, brightest on breast. Voice Song is fast ascending series of 14-20 notes, levelling off on the last 4-5, in 2-3 seconds. Female song similar but shorter. Also short, barking call.

Assessment Information [top]

Red List Category & Criteria: Vulnerable B2ab(i,ii,iii,iv,v); C2a(i) ver 3.1
Year Published: 2017
Date Assessed: 2017-10-01
Assessor(s): BirdLife International
Reviewer(s): Symes, A.
Contributor(s): Kirwan, G., Whitney, B., Whittaker, A., Willis, E. & da Silva, J.
Facilitator/Compiler(s): Capper, D., Pople, R., Sharpe, C.J., Symes, A., Wheatley, H., Westrip, J.
Justification:
The widespread destruction of suitable deciduous forest has reduced this species's now small population and (poorly understood) range (Collar et al. 1992). Remaining populations are severely fragmented and the species qualifies as Vulnerable.

Previously published Red List assessments:

Geographic Range [top]

Range Description:Herpsilochmus pectoralis possesses an unusual and highly fragmented range in north-east Maranhão (most recently, Axixá in the 1980s, Bacabal in 1974 [E. O. Willis in litt 1999] and Fazenda do Caimbo in 1972), east Rio Grande do Norte (23 sites in 12 municipalities in 2005-2007 [Silva 2007]), Sergipe (Itabaiana in 1991), Paraiba (first state record in Guaju in 2004 [Perreira et al. 2005]) and north-east Bahia (eight localities, five with records since 1980 [J. M. C. da Silva in litt. 1995, G. M. Kirwan in litt. 1999, A. Whittaker in litt. 1999]), north-east Brazil. It is clearly extremely local and is considered to have disappeared from a large part of its former range (B. Whitney in litt. 2017). However, although overall numbers are presumably not high, it is fairly common at some sites in Bahia. Tracewski et al. (2016) estimated the maximum Area of Occupancy (calculated as the remaining tree area within the species’s range) to be c.1,850 km2, rounded here to 1,900 km2.
Countries occurrence:
Native:
Brazil
Additional data:
Estimated area of occupancy (AOO) - km2:1900Continuing decline in area of occupancy (AOO):Yes
Extreme fluctuations in area of occupancy (AOO):NoEstimated extent of occurrence (EOO) - km2:879000
Continuing decline in extent of occurrence (EOO):YesExtreme fluctuations in extent of occurrence (EOO):No
Number of Locations:11-100Continuing decline in number of locations:Yes
Extreme fluctuations in the number of locations:No
Upper elevation limit (metres):850
Range Map:Click here to open the map viewer and explore range.

Population [top]

Population:The population is estimated to number 2,500-9,999 mature individuals based on an assessment of known records, descriptions of abundance and range size. This is consistent with recorded population density estimates for congeners or close relatives with a similar body size, and the fact that only a proportion of the estimated Extent of Occurrence is likely to be occupied. This estimate is equivalent to 3,750-14,999 individuals, rounded here to 3,500-15,000 individuals. Densities of 60-113 birds/km2 have been found (Silva 2007).

Trend Justification:  Forest loss within the species's range has been estimated at c.3.4% over 3 generations (c.14 years) (Tracewski et al. 2016). Therefore, the rate of decline in this species is suspected to be <10% over 3 generations.
Current Population Trend:Decreasing
Additional data:
Number of mature individuals:2500-9999Continuing decline of mature individuals:Yes
Extreme fluctuations:NoPopulation severely fragmented:Yes
No. of subpopulations:2-100Continuing decline in subpopulations:Yes
Extreme fluctuations in subpopulations:NoAll individuals in one subpopulation:No
No. of individuals in largest subpopulation:1-89

Habitat and Ecology [top]

Habitat and Ecology:It inhabits gallery forest and deciduous forest in Maranhão, and tall caatinga woodland and closed, old secondary forest in Bahia. It survives in remnant woodlots characterised by numerous trees over 10 m, and often 15-20 m, but is not found in adjacent habitats with smaller trees. Some of these woodlots are moderately grazed, but it only occurs where there is still a fairly well developed understorey.

Systems:Terrestrial
Continuing decline in area, extent and/or quality of habitat:Yes
Generation Length (years):4.8
Movement patterns:Not a Migrant

Threats [top]

Major Threat(s): It is still insufficiently known to determine precise threats, but clearance for irrigated and dry field agriculture has removed extensive tracts of deciduous forest (da Silva and Oren 1997). The high biomass of these forests makes them important sources of charcoal for Brazil's steel and pig-iron industries, and supposedly substitute plantations of Eucalyptus sp. are being used by the paper pulp industry (da Silva and Oren 1997). Intensive grazing and extensive burning are widespread throughout its range.

Conservation Actions [top]

Conservation Actions: Conservation Actions Underway
It is protected under Brazilian law and occurs in Serra de Itabaiana Ecological Station, Sergipe, and Chapada da Diamantina National Park, Bahia (Wege and Long 1995). Logging trucks were observed extracting timber from the latter in February 1996 (A. Whittaker in litt. 1999), indicating that protection is inadequate.

Conservation Actions Proposed
Survey to improve knowledge of its distribution and habitat requirements. Survey Serra de Itabaiana for this and other threatened species. Map and ecologically evaluate extant patches of deciduous forest (da Silva and Oren 1997), especially in Bahia. Conduct long-term studies on the ecology of this species's forests (e.g. succession and selective logging) to develop viable strategies for economic utilisation (da Silva and Oren 1997). Create a system of conservation units (following surveys and mapping) that adequately protects the species, including the site 23 km from Jeremoaba in Bahia, an area in central Maranhão and the de facto protection and expansion of Chapada da Diamantina National Park to include known sites just outside the park's boundaries.


Citation: BirdLife International. 2017. Herpsilochmus pectoralis. The IUCN Red List of Threatened Species 2017: e.T22701577A118816985. . Downloaded on 12 December 2017.
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