Ploceus burnieri 

Scope: Global
Language: English

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Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Aves Passeriformes Ploceidae

Scientific Name: Ploceus burnieri Baker & Baker, 1990
Common Name(s):
English Kilombero Weaver
French Tisserin de Kilombéro
Taxonomic Source(s): del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A., Fishpool, L.D.C., Boesman, P. and Kirwan, G.M. 2016. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 2: Passerines. Lynx Edicions and BirdLife International, Barcelona, Spain and Cambridge, UK.
Identification information: 14-15 cm. Medium-sized, green-and-yellow weaver. Male nape and underparts bright yellow. Contrasting, small black mask extends only to eye and onto throat, narrowly bordered by chestnut. Dark eye. Female dull version of male, lacks black face. Black bill. Brownish-flesh legs. Similar spp. Northern Masked-weaver P. taeniopterus less bright golden-yellow, more chestnut around black mask. Voice Typical weaver-like squizzling and buzzing sounds.

Assessment Information [top]

Red List Category & Criteria: Vulnerable B1ab(iii,v);C2a(ii) ver 3.1
Year Published: 2016
Date Assessed: 2016-10-01
Assessor(s): BirdLife International
Reviewer(s): Butchart, S. & Symes, A.
Contributor(s): Baker, N., Burgess, N., Rainey, H. & Tye, A.
Facilitator/Compiler(s): Benstead, P., Ekstrom, J., Evans, M., Shutes, S., Starkey, M., Symes, A., Taylor, J. & Westrip, J.
This species has a small, fragmented range, within which habitat loss and/or increased pesticide use are suspected to be causing a continuing decline in its small population. The species is therefore considered Vulnerable. Habitat loss may accelerate with increased agricultural development and this species should be monitored to assess whether its threat status needs to be upgraded.

Previously published Red List assessments:

Geographic Range [top]

Range Description:Ploceus burnieri, first discovered in 1986, has a very small range, being confined to the Kilombero river floodplain in south-central Tanzania (Baker and Baker 1990). It has a patchy and restricted distribution within its range, but is abundant in suitable habitat (H. Rainey in litt. 1999).

Countries occurrence:
Tanzania, United Republic of
Additional data:
Continuing decline in area of occupancy (AOO):Unknown
Extreme fluctuations in area of occupancy (AOO):NoEstimated extent of occurrence (EOO) - km2:2400
Continuing decline in extent of occurrence (EOO):UnknownExtreme fluctuations in extent of occurrence (EOO):No
Number of Locations:6-10Continuing decline in number of locations:Unknown
Extreme fluctuations in the number of locations:NoLower elevation limit (metres):250
Upper elevation limit (metres):250
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 in total, rounded here to 3,500-15,000 individuals.

Trend Justification:  The species's population is suspected to be in decline owing to the continued conversion of swamps in the Kilombero river floodplain for cultivation and pasture. The likely rate of decline has not been estimated.
Current Population Trend:Decreasing
Additional data:
Number of mature individuals:2500-9999Continuing decline of mature individuals:Yes
Extreme fluctuations:NoPopulation severely fragmented:No
No. of subpopulations:1Continuing decline in subpopulations:No
Extreme fluctuations in subpopulations:NoAll individuals in one subpopulation:Yes
No. of individuals in largest subpopulation:100

Habitat and Ecology [top]

Habitat and Ecology:It occurs in extensive riverside swamps fringed with tall reedbeds Phragmites, generally in areas away from trees (possibly related to competition with the African Golden-Weaver P. subaureus) (H. Rainey in litt. 1999). It has been observed foraging in groups on the ground prior to flooding (Baker and Baker 1990). It may also be found in areas of grassland away from the Kilombero River, and can tolerate some disturbance (Ntongani and Andrew 2013; Rannestad et al. 2015). The diet includes flowering and fruiting grass-heads, as well as dried fish and domestic refuse (H. Rainey in litt. 1999). Nests are in loose groups of up to 20 (occasionally 30), each being attached to a single reed-stem, frequently overhanging water, in areas of seasonal flooding (H. Rainey in litt. 1999). Clutch-size is apparently 1-2 (Baker and Baker 1990).

Systems:Terrestrial; Freshwater
Continuing decline in area, extent and/or quality of habitat:Yes
Generation Length (years):4
Movement patterns:Not a Migrant

Threats [top]

Major Threat(s): The extent of dry-season cultivation in the centre of the floodplain is increasing and use of the central portion of the Kilombero Valley by pastoralists is increasing rapidly (H. Rainey in litt. 1999). As well as the resulting habitat loss, dry-season burning, to clear fields and to promote growth of new grass for cattle, may have a negative impact (H. Rainey in litt. 1999). Grazing may also affect habitat directly (H. Rainey in litt. 2007). A expanding area of unknown size in the north of the Kilombero Valley has been converted for large-scale sugar cane cultivation (N. Burgess in litt. 2007, H. Rainey in litt. 2007), with up to 200 km2 predicted to be converted in the near future (H. Rainey in litt. 1999). Individual farmers supply the sugar cane processing plant and are less likely to be limited by any pesticide or planning laws than the industrial plantations (H. Rainey in litt. 2007). Additionally, rice farming is expanding and could affect the species's habitat (H. Rainey in litt. 2007). Increases in pesticide- or fertiliser-use in the catchment may have negative impacts on the species and its habitat (H. Rainey in litt. 1999). However, apparently no studies of the effects of pesticides or fertilisers on wildlife have been carried out (H. Rainey in litt. 2007). While this species may be able to tolerate some habitat disturbance (Ntongani and Andrew 2013), it has such a restricted range that threats could affect a large proportion of the population at once and lead to very rapid declines.

Conservation Actions [top]

Conservation Actions: Conservation Actions Underway
The Kilombero Valley has recently been declared a Ramsar site, with funding allocated from the Wildlife Department (N. Burgess in litt. 2007). It was formerly designated a Game Controlled Area, which only restricted the hunting of large animals, and not land-use (e.g. commercial agriculture) that might be deleterious for this species. Game Controlled Areas have been replaced by Wildlife Management Areas. However, the status of the valley is uncertain (N. Burgess in litt. 2007).

Conservation Actions Proposed
Carry out surveys in order to assess the species's population size. Establish a scheme for monitoring its population. Assess its habitat requirements. Evaluate the potential effects of increased pesticide- and fertiliser-use and of dry-season burning. Lobby government for improved status of the Kilombero Valley protected area as its current status is seen to be failing conservation and wildlife (H. Rainey in litt. 2007). Carry out management planning in the valley including zoning plans for industry, agriculture, livestock grazing and wildlife (H. Rainey in litt. 2007).

Citation: BirdLife International. 2016. Ploceus burnieri. The IUCN Red List of Threatened Species 2016: e.T22718856A94599591. . Downloaded on 22 May 2018.
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