Biometrics of the Southern Grey Shrike Lanius Meridionalis in Relation to Age and Sex

Total Page:16

File Type:pdf, Size:1020Kb

Biometrics of the Southern Grey Shrike Lanius Meridionalis in Relation to Age and Sex Ringing & Migration (2007) 23, 141-146 Biometrics of the Southern Grey Shrike Lanius meridionalis in relation to age and sex FRANCISCO GUTIÉRREZ-CORCHERO1, FRANCISCO CAMPOS2, M. ÁNGELES HERNÁNDEZ1* and ANA AMEZCUA1 1Department of Zoology & Ecology, Faculty of Sciences, University of Navarre, E-31080 Pamplona, Spain 2European University Miguel de Cervantes, c/ Padre Julio Chevalier 2, E-47012 Valladolid, Spain The biometrics of Southern Grey Shrike Lanius meridionalis and differences from the closely related Great Grey Shrike L. excubitor are poorly characterised. The aim of this study was to describe sex and age vari- ation in external biometric measurements for the nominate Southern Grey Shrike L. m. meridionalis in a population from northern Spain. In total, 174 Southern Grey Shrikes were ringed, measured, and sexed by molecular techniques. The overall biometry of the shrikes was summarised by Principal Components Analysis (PCA). There were significant differences in size between sex and age classes. We observed a sexual dimorphism in size, with adult males the largest and yearling females the smallest. According to the PCA, only the first principal component showed significant sex and age differences, and these were related to the tail, wing, third primary, white on primaries and white on rectrices. According to these data, and at least in terms of biometry, the Southern Grey Shrike is more similar to the Loggerhead Shrike L. ludovicianus than to the Great Grey Shrike. The Southern Grey Shrike Lanius meridionalis is a socially (Infante & Peris 2004). The goal of this study was to provide monogamous passerine without obvious sexual dimorphism a detailed description of the biometrics of the nominate in plumage. Ten subspecies have been described, with a Southern Grey Shrike in relation to sex and age of live largely Afro–Asian distribution, and the nominate L. m. animals, and to compare the results with other populations meridionalis is mostly found in the Iberian Peninsula and and closely related species. southeastern France (Lefranc & Worfolk 1997, Harris & Franklin 2000). In the Iberian Peninsula it is sedentary (Hernández 1999). According to Isenmann & Bouchet METHODS (1993), the Southern Grey Shrike is a different species from the Great Grey Shrike, and this has been accepted Study site and capture methods by taxonomic authorities (British Ornithologists’ Union We captured 174 shrikes during January–December 1997). Both species are part of a superspecies Lanius (1999–2002) in the province of Navarre (northern Spain). [excubitor] that includes the Chinese Great Grey Shrike L. Birds were captured using a variation of the Potter trap sphenocercus and the Loggerhead Shrike L. ludovicianus in (Craig 1997), ringed, measured and sexed. North America (Panov 1995, Schön 1998). The taxonomic separation between the Southern Grey Shrike and Great Biometrics and age determination Grey Shrike is based on morphological, ecological and The following body measurements were taken according to behavioural differences (Isenmann & Bouchet 1993, Panov Svensson (1992): the length of the wing (maximum chord), 1995, Schön 1998). More recently, genetic differences have third primary (3P) and tail feathers were measured with a also been described (Hernández et al 2004). 0.5 mm precision ruler; the length of the tarsus, middle Nonetheless, little is known about the biometrics of the toe and bill height, width and length (from the tip to Southern Grey Shrike. The only information available the distal edge of nostrils) were measured with a 0.1 mm is based on measurements of a few museum specimens precision calliper. We also measured the extent of white (Cramp & Perrins 1993) and, more recently, on a study on the primaries (WP, from distal edge of basal white area of live animals from the central-west Iberian Peninsula to wrist) and on the rectrices (WR, greatest length of white spot on inner web of the distal end of outer rectrix) (Fig 1) * Correspondence author with a 0.5 mm precision ruler as described by Collister & Email: [email protected] Wicklum (1996). In each shrike, both WP and WR were © 2007 British Trust for Ornithology 142 F. Gutiérrez-Corchero et al measured three times and the final value used for analysis The birds were classified as yearlings or adults. The was the average of these three measurements. Finally, yearlings (Euring age codes 3 or 5) had undergone a partial birds were weighed using a 0.1 g precision balance. Not moult in summer and winter (Svensson 1992) resulting in all measurements were taken on all birds and, therefore, a significant colour contrast in the wing feathers: newly the sample size varied. Weight was not considered in the moulted, shiny-black greater, median and lesser coverts analysis since it can vary substantially during the breeding contrasting with unmoulted black-brownish primaries, period (Collister & Wicklum 1996, Takagi 1996), but the secondaries and primary coverts (retained juvenile average value is reported. feathers). The adults were two or more years old (Euring Figure 1. Pattern of wings and tail in the Southern Grey Shrike, Figure 2. Mean scores for the three Principal Component axes by showing the white wing patch at the base of the primaries and the sex and age of Southern Grey Shrikes in northern Spain. Error bars: white at the end of the outer rectrices. ± standard error. © 2007 British Trust for Ornithology, Ringing & Migration, 23, 141-146 Biometrics of Southern Grey Shrike 143 Table 1. Average values (± standard deviation [sd]) of the variables measured in the Southern Grey Shrike in northern Spain according to sex and age with, in brackets, the sample size and range of values. Measurements are in mm, weight in g. WP: white on primaries. WR: white on rectrices. 3P: third primary. Males Females adults yearlings adults yearlings All birds Wing 106.30 ± 1.53 103.45 ± 1.35 105.64 ± 1.63 102.65 ± 1.74 104.61 ± 2.22 (51; 104–111) (30; 100–106) (44; 102–109) (49; 99–106) (174; 99–111) WP 55.16 ± 1.73 54.35 ± 1.47 54.91 ± 1.12 53.08 ± 1.64 54.65 ± 1.92 (48; 52.2–59.5) (28; 51.5–57.5) (43; 53.0–58.0) (48; 49.5–56.5) (167; 49.5–59.5) 3P 80.38 ± 1.54 77.89 ± 1.85 79.50 ± 1.56 77.60 ± 1.25 78.95 ± 1.92 (49; 77.5–84.0) (29; 74.0–82.0) (43; 75.5–82.0) (47; 75.0–80.0) (168; 74.0–84.0) Tail 116.78 ± 2.80 112.60 ± 2.63 114.02 ± 2.23 110.30 ± 3.34 113.50 ± 3.74 (48; 112.0–125.0) (29; 107.0–117.0) (43; 108.0–118.0) (48; 101.0–118.0) (168; 101.0–125.0) WR 49.33 ± 5.21 47.62 ± 5.00 45.40 ± 3.50 45.38 ± 4.29 46.91 ± 4.81 (48; 34.0–58.0) (28; 37.5–55.5) (43; 39.5–53.5) (46; 29.2–53.5) (165; 29.2–58.0) Bill length 14.13 ± 0.64 14.07 ± 0.59 13.90 ± 0.63 13.78 ± 0.63 13.96 ± 0.64 (51; 12.65–15.53) (30; 13.05–15.04) (44; 12.49–15.30) (49; 12.55–15.13) (174; 12.49–15.53) Bill depth 8.94 ± 0.19 8.86 ± 0.21 8.88 ± 0.20 8.83 ± 0.21 8.88 ± 0.20 (51; 8.39–9.30) (30; 8.46–9.25) (43; 8.44–9.30) (49; 8.37–9.45) (173; 8.37–9.45) Bill width 6.82 ± 0.23 6.83 ± 0.28 6.92 ± 0.31 6.80 ± 0.28 6.84 ± 0.27 (51; 6.37–7.22) (30; 6.30–7.50) (43; 6.40–7.56) (49; 6.00–7.35) (173; 6.00–7.56) Tarsus 29.92 ± 0.57 29.71 ± 0.69 29.88 ± 0.65 29.78 ± 0.59 29.83 ± 0.62 (51; 28.72–31.43) (30; 28.16–30.90) (44; 28.23–31.49) (49; 28.30–31.24) (174; 28.23–31.49) Middle toe 20.46 ± 0.65 20.40 ± 0.63 20.70 ± 0.56 20.51 ± 0.62 20.52 ± 0.62 (49; 18.09–21.95) (29; 19.14–21.75) (42; 19.71–21.75) (48; 18.50–21.48) (168; 18.09–21.95) Weight 62.26 ± 2.84 61.56 ± 2.92 63.98 ± 2.61 63.17 ± 2.57 62.80 ± 2.84 (51; 55.5–69.5) (30; 56.5–68.5) (40; 58.5–69.0) (47; 57.0–69.5) (168; 55.5–69.5) age codes 4 or 6) and lacked colour contrast on the wing (2002). DNA sequences corresponding to the Chromo- feathers as a result of a complete moult in summer after Helicase-DNA-Binding (CHD) protein (present in Z and breeding (Svensson 1992). These criteria were validated W sex chromosomes) were amplified using the Polymerase by comparing birds of known age that had been ringed Chain Reaction (PCR). PCR fragments were separated by as nestlings. gel electrophoresis on a 2.5% agarose gel, viewed under UV light and photographed (Gutiérrez-Corchero et al Sex determination 2002). According to Griffiths et al (1998), blood samples Blood samples (0.1 ml) were obtained by brachial with one DNA band (corresponding to the CHD-Z gene) venipuncture and placed on FTA® Classic Cards until indicate males, and samples with two bands (corresponding DNA extraction, according to Gutiérrez-Corchero et al to CHD-Z and CHD-W genes) are females. © 2007 British Trust for Ornithology, Ringing & Migration, 23, 141-146 144 F. Gutiérrez-Corchero et al Table 2.
Recommended publications
  • First Record of Brown Shrike (Lanius Cristatus) in British Columbia. by Rick Toochin, Peter Hamel and Margo Hearne. Submitted: April 15, 2018
    First record of Brown Shrike (Lanius cristatus) in British Columbia. By Rick Toochin, Peter Hamel and Margo Hearne. Submitted: April 15, 2018. Introduction and Distribution The Brown Shrike (Lanius cristatus) is a small species that is found throughout East Asia breeding south of the northern tundra from Eastern Chukotka Peninsula, Kamchatka Peninsula, Sea of Okhotsk, Japan, Korea, China, from northern Mongolia westward into Central Siberia approximately Yenisei and Anadyr Rivers (Lewington et al. 1992, Brazil 2009, Pyle et al. 2015). This species is highly migratory throughout its vast range. The Brown Shrike winters from India to southern China, Indonesia, and the Philippines (Lewington et al. 1992). There are 4 subspecies of Brown Shrike found throughout this species range. These include the nominate subspecies of Brown Shrike is (Lanius cristatus cristatus) which is found breeding from eastern Siberia to northwestern Mongolia. This subspecies is highly migratory and travels far to the wintering grounds (Pyle et al. 2015). This subspecies winters in India, Bhutan, Nepal, Bangladeshi, Burma, Laos, Thailand, and Cambodia, southern Vietnam and the Malayan Peninsula (Pyle et al. 2015, Clements et al. 2016). The first Alaska record was tentatively identified as (L. c. lucionensis) (Gibson 1981), but has subsequently been identified as nominate (L. c. cristatus) (Gibson and Withrow 2015). This is the subspecies that now widely accepted as the subspecies that accounts for most, if not all North American records (Hamilton et al. 2007). The second subspecies of Brown Shrike is (Lanius cristatus confuses) which is found breeding in Manchuria and Amurland (Clements et al. 2016). This subspecies winters in Southeast Asia on the Malayan Peninsula and Sumatra (Clements et al.
    [Show full text]
  • Brief Report Red-Backed Shrike (Lanius Collurio)
    Ornis Fennica 83:181186. 2006 Brief report Red-backed Shrike (Lanius collurio) nest performance in a declining British population: a comparison with a stable population in Poland Piotr Tryjanowski*, Tim H. Sparks & Humphrey Q.P. Crick Tryjanowski, P., Institute of Environmental Biology, Adam Mickiewicz University, Umultowska 89, PL-61-614 Poznañ, Poland. [email protected] (* Corresponding au- thor) Sparks, T.H., NERC Centre for Ecology and Hydrology, Monks Wood, Abbots Ripton, Huntingdon, Cambridgeshire PE282LS, UK Crick, H.Q.P., British Trust for Ornithology, The Nunnery, Thetford, IP24 2PU, UK Received 17 May 2006, revised 28A ugust 2006, accepted 11 October 2006 We compare the breeding ecology of Red-backed Shrike Lanius collurio prior to its effec- tive extinction (in 1990) as a breeding bird in the UK with that of a stable population in southwestern Poland. We use breeding performance data derived from the UK and Polish Nest Record Schemes. Although the clutch size in the UK was slightly smaller than in Po- land (4.52 ± 0.09 and 4.79 ± 0.11, respectively), brood sizes of UK nests were signifi- cantly larger (3.21 ± 0.14 v.s. 2.21 ± 0.23) than those from Poland. These data do not sug- gest that poor breeding performance drove the population decline in the UK. We argue that other evidence suggests that egg collecting and delayed phenology may have contrib- uted to the extinction, although we have been unable to assess the influence of other pos- sible factors such as predation and post-fledging survival. 1. Introduction (Sharrock 1976) but its breeding range had de- clined by 86% by the next atlas in 198891, with The Red-backed Shrike Lanius collurio was for- breeding confirmed in only 2 10-km squares merly widespread in farmland, scrub and heath- (Bibby 1993).
    [Show full text]
  • The Common Cuckoo Is an Effective Indicator of High Bird Species
    www.nature.com/scientificreports OPEN The common cuckoo is an effective indicator of high bird species richness in Asia and Europe Received: 16 February 2017 Federico Morelli1, Anders Pape Møller2, Emma Nelson3, Yanina Benedetti1, Wei Liang 4, Accepted: 19 May 2017 Petra Šímová 1, Marco Moretti5 & Piotr Tryjanowski6 Published: xx xx xxxx Common cuckoo Cuculus canorus is a charismatic bird species with a dominant presence in human culture: from folklore legends to nowadays there is evidence of cuckoos being a prime candidate as a surrogate of bird diversity. Recent studies demonstrated that the cuckoo can predict hotspots of taxonomic diversity and functional diversity of bird communities in European countries. In this study, we demonstrated that the cuckoo is an excellent bioindicator at multi-spatial scale, extending cuckoo surrogacy from Europe to Asia. Even using three different survey methods (transect, square, point counts), comparing the new findings with results of our research in Europe, sites where the cuckoo is present were characterized by greater species richness, while the cuckoo was absent from sites with low species richness. The goodness of fit of models based on point counts ranged between 71 and 92%. Furthermore, the cuckoo population trend mirrors the average population trend and climate suitability of overall bird communities in Europe. The common cuckoo is therefore a suitable intercontinental bioindicator of hotspots of bird richness, even under climate change scenarios or in areas where the species co-occurs with other cuckoo species, opening a new avenue for standardized citizen science on bird biodiversity surveys worldwide. Why is the common cuckoo Cuculus canorus a fascinating bird species for humans? What are the main reasons for the species being known as “a messenger of spring and morality”1, and why is it so conspicuous in human culture? A review of folklore shows clearly that the enigmatic cuckoo has driven the collective imagination of people throughout the world for thousands of years.
    [Show full text]
  • Bird Species Recorded in Alvechurch Parish 2010-2016 A) Total in Grid Squares SP0172, SP0272, SP0273, SP0274, SP0275, SP0276, SP
    Bird Species Recorded in Alvechurch Parish 2010-2016 A) Total in grid squares SP0172, SP0272, SP0273, SP0274, SP0275, SP0276, SP0370, SP0371, SP0372, SP0374, SP0375, SP0376, SP0469, SP0470, SP0471, SP0472, SP0473, SP0474, SP0475, SP0476, SP0569, SP0570, SP0571, SP0572, SP0573, SP0574, SP0575 Barn Owl Green Sandpiper Pochard Barnacle Goose Green Woodpecker Red Kite Blackbird Greenfinch Redshank Blackcap Grey Heron Redwing Black-headed Gull Grey Wagtail Reed Bunting Blue Tit Greylag Goose Reed Warbler Bullfinch Herring Gull Ring Ouzel Buzzard Hobby Robin Canada Goose House Martin Rook Carrion Crow House Sparrow Sand Martin Caspian Gull Jackdaw Scaup Chaffinch Jay Sedge Warbler Chiffchaff Kestrel Shoveler Coal Tit Kingfisher Siskin Collared Dove Lapwing Skylark Common Gull Lesser Black-backed Gull Smew Common Sandpiper Lesser Redpoll Snipe Common Tern Lesser Whitethroat Song Thrush Coot Linnet Sparrowhawk Cormorant Little Egret Starling Cuckoo Little Grebe Stock Dove Curlew Little Owl Stonechat Dunnock Long-tailed Tit Swallow Feral Pigeon Magpie Swift Fieldfare Mallard Teal Gadwall Mandarin Treecreeper Garden Warbler Meadow Pipit Tufted Duck Goldcrest Mistle Thrush Turnstone Golden Plover Moorhen Wheatear Goldeneye Mute Swan Whitethroat Goldfinch Nuthatch Wigeon Goosander Osprey Willow Warbler Great Crested Grebe Oystercatcher Wood Pigeon Great Grey Shrike Peregrine Woodcock Great Northern Diver Pheasant Wren Great Spotted Woodpecker Pied Wagtail Yellowhammer Great Tit Bird Species Recorded in Alvechurch Parish 2010-2016 B) Individual grid
    [Show full text]
  • Does Experimentally Simulated Presence of a Common Cuckoo (Cuculus Canorus) Affect Egg Rejection and Breeding Success in the Red‑Backed Shrike (Lanius Collurio)?
    acta ethologica (2021) 24:87–94 https://doi.org/10.1007/s10211-021-00362-1 ORIGINAL PAPER Does experimentally simulated presence of a common cuckoo (Cuculus canorus) affect egg rejection and breeding success in the red‑backed shrike (Lanius collurio)? Piotr Tryjanowski1,2 · Artur Golawski3 · Mariusz Janowski1 · Tim H. Sparks1,4 Received: 23 September 2020 / Revised: 18 January 2021 / Accepted: 10 February 2021 / Published online: 8 March 2021 © The Author(s) 2021 Abstract Providing artifcial eggs is a commonly used technique to understand brood parasitism, mainly by the common cuckoo (Cuculus canorus). However, the presence of a cuckoo egg in the host nest would also require an earlier physical presence of the common cuckoo within the host territory. During our study of the red-backed shrike (Lanius collurio), we tested two experimental approaches: (1) providing an artifcial “cuckoo” egg in shrike nests and (2) additionally placing a stufed common cuckoo with a male call close to the shrike nest. We expected that the shrikes subject to the additional common cuckoo call stimuli would be more sensitive to brood parasitism and demonstrate a higher egg rejection rate. In the years 2017–2018, in two locations in Poland, a total of 130 red-backed shrike nests were divided into two categories: in 66 we added only an artifcial egg, and in the remaining 64 we added not only the egg, but also presented a stufed, calling common cuckoo. Shrikes reacted more strongly if the stufed common cuckoo was present. However, only 13 incidences of egg acceptance were noted, with no signifcant diferences between the locations, experimental treatments or their interaction.
    [Show full text]
  • First North American Sighting of Brown Shrike, (Lanius Cristatus) and Dusky Warbler (Phylloscopus Fuscatus), and Second Record O
    F/rst North American Sighting of Brown Shrike, (Lanius cristatus) and Dusky Warbler (Phylloscopus fuscatus), and second record of Red-throad Flyca. her (Ficedula pavva) Ben King, Davis Finch, Richard Stallcupand Will Russell HtEFOLLOWING SIGHTINGS weremade by not reaching the coast), to the mouth of the he authorswhile leading birding tours White River in Anadyr' Valley and upper near Gambell, St. Lawrence Island in the reaches of the River Achay-Vayam in northern Bering Sea in June 1977. Scientific Koratskaya Zemlya, and occurs sporadically nomenclature follows Vaurie (1959) and in Kamchatka (Dement'ev et al., 1968 and English names are those of King and Ivanov, 1976). We could not see any white Dickinson (1975). frontal band in the field. L. c. cristatus has a narrow inconspicuousfrontal band whereas Brown Shrike, Lanius cristatus. A single all three of the other races listed by Vaurie bird was observed on June 4, 5 and 6, 1977 (1959) have broad, more conspicuousones about 0.7 km east of Gambell. All observa- tions were within a radius of 300 m on level Dusky Warbler, Phylloscopusfuscatus gravel containing some grass up to 25 cm One was seen about 4 km south-southeastof high, and adjacent to a boulder-strewntun- Gambell on June 6, 1977by about 15 observ- dra-covered hillside. The bird choseexposed ers. We watched it for about 1« hours percheson knolls and boulders.It was quite through scopesand binocularsgenerally shy but well observed through several at a distance of 30 - 40 m, but several times 20x-40x spotting scopes at distances of as close as approximately7 - 8 m.
    [Show full text]
  • Preliminary Survey of the Avifauna of Mt Tchabal Mbabo, West-Central Cameroon THOMAS BATES SMITH and DUNCAN Mcniven
    Bird Conservation International (1993) 3:13-19 Preliminary survey of the avifauna of Mt Tchabal Mbabo, west-central Cameroon THOMAS BATES SMITH and DUNCAN McNIVEN Summary The montane forests of western Cameroon are well known for their endemic birds. The most northerly such forests probably occur on Mt Tchabal Mbabo, where a preliminary survey of the avifauna in 1990 found 12 montane species, of which six represented significant range extensions, among them the threatened Ploceus bannermani. Given the increasing human pressures on other montane forests in Cameroon, Mt Tchabal Mbabo may be attractive for future conservation because of its comparative lack of human dis- turbance. Densities of indigenous people are low and there is a lack of significant hunting and firewood-gathering, the precipitous nature of the northern slope makes human intrusions difficult, and the lack of human disturbance may mean that local animal populations are stable. Les forets d'altitude de l'ouest du Cameroun sont bien connues pour leurs populations endemiques d'oiseaux. Les forets les plus au nord sont celles du Mont Tchabal Mbabo, ou un recensement preliminaire de la faune aviaire en 1990 a revele 12 especes, dont six avaient une aire de repartition relativement grande, y compris l'espece menacee Ploceus bannermani. Etant donne l'accroissement des pressions humaines sur les autres forets d'altitude au Cameroun, le Mont Tchabal Mbabo pourrait se reveler interessant pour des programmes de conservation futurs, compte tenu d'une perturbation humaine relat- ivement inexistante. Les densites de population indigene y sont faibles, et la chasse ainsi que le ramassage du bois pour les besoins domestiques ne sont pas significatifs.
    [Show full text]
  • Status of the Great Grey Shrike in Britain and Ireland
    Status of the Great Grey Shrike in Britain and Ireland Peter Fraser and John Ryan The Great Grey Shrike Lanius excubitor is a widespread Holarctic species. The nominate race breeds from Scandinavia and France east to western Siberia, northern populations exhibiting a winter dispersal or short-distance migration to warmer areas, including Britain and Ireland (Cramp & Perrins 1993). Its status in these last countries has not been investigated in detail until comparatively recently. This paper attempts to estimate the current numbers of this attractive shrike visiting these islands. Historical perspective In the first half of the twentieth century, when there were far fewer observers than there are today, records of Great Grey Shrike in Britain seemed to be rather scarce. Bannerman (1953) suggested that the Great Grey Shrike might be 'even [an] annual visitor to our shores'. Two decades later, it was described as both a passage migrant and a winter visitor in 'small, rather variable numbers', being most numerous on the East Coast in October, with most wintering individuals occurring in Scotland (BOU 1971). The first systematic attempt to assess the British wintering population was made during 1981-84, with the Winter Atlas (Lack 1986): records were found to be much more widespread in midwinter than had previously been supposed, and the wintering population was estimated at a minimum of 150 individuals. In Britain, the Great Grey Shrike has long been characterised by considerable annual fluctuations in its numbers. The available records nevertheless suggest that there has been a general decline over the last 40 or more years, and particularly since the 1970s.
    [Show full text]
  • European Red List of Birds
    European Red List of Birds Compiled by BirdLife International Published by the European Commission. opinion whatsoever on the part of the European Commission or BirdLife International concerning the legal status of any country, Citation: Publications of the European Communities. Design and layout by: Imre Sebestyén jr. / UNITgraphics.com Printed by: Pannónia Nyomda Picture credits on cover page: Fratercula arctica to continue into the future. © Ondrej Pelánek All photographs used in this publication remain the property of the original copyright holder (see individual captions for details). Photographs should not be reproduced or used in other contexts without written permission from the copyright holder. Available from: to your questions about the European Union Freephone number (*): 00 800 6 7 8 9 10 11 (*) Certain mobile telephone operators do not allow access to 00 800 numbers or these calls may be billed Published by the European Commission. A great deal of additional information on the European Union is available on the Internet. It can be accessed through the Europa server (http://europa.eu). Cataloguing data can be found at the end of this publication. ISBN: 978-92-79-47450-7 DOI: 10.2779/975810 © European Union, 2015 Reproduction of this publication for educational or other non-commercial purposes is authorized without prior written permission from the copyright holder provided the source is fully acknowledged. Reproduction of this publication for resale or other commercial purposes is prohibited without prior written permission of the copyright holder. Printed in Hungary. European Red List of Birds Consortium iii Table of contents Acknowledgements ...................................................................................................................................................1 Executive summary ...................................................................................................................................................5 1.
    [Show full text]
  • Stephens Forest
    Field Checklist for Stephens Forest ___Warbling Vireo* ___Kentucky Warbler* * = confirmed or likely area breeder ___Red-eyed Vireo* ___Common Yellowthroat* Iowa Wildlife Action Plan Migratory Species of Greatest ___Hooded Warbler* Stephens Forest Conservation Need ___Blue Jay* ___American Redstart* Iowa Wildlife Action Plan Nesting Species of Greatest ___American Crow* ___Cerulean Warbler* Conservation Need ___Northern Parula* ___Horned Lark* ___Magnolia Warbler ___Greater White-fronted Goose ___Ring-billed Gull ___Bay-breasted Warbler Bird Conservation ___Snow Goose ___Purple Martin* ___Blackburnian Warbler ___Cackling Goose ___Rock Pigeon* ___Tree Swallow* ___Yellow Warbler* ___Canada Goose* ___Eurasian Collared-Dove* ___N. Rough-winged Swallow* ___Chestnut-sided Warbler* Area ___Wood Duck* ___Mourning Dove* ___Bank Swallow* ___Blackpoll Warbler ___Gadwall ___Cliff Swallow* ___Yellow-rumped Warbler ___American Wigeon ___Yellow-billed Cuckoo* ___Barn Swallow* ___Yellow-throated Warbler ___Mallard ___Black-billed Cuckoo* ___Black-throated Green Warbler ___Blue-winged Teal ___Black-capped Chickadee* ___Canada Warbler ___Northern Shoveler ___Barn Owl ___Tufted Titmouse* ___Wilson’s Warbler ___Hooded Merganser ___Yellow-breasted Chat* Belted Kingfisher ___Common Merganser ___Eastern Screech-Owl* ___Red-breasted Nuthatch USFWS ___Great Horned Owl* ___White-breasted Nuthatch* ___Eastern Towhee* ___Northern Bobwhite* ___Barred Owl* ___American Tree Sparrow ___Ring-necked Pheasant* ___Long-eared Owl ___Brown Creeper ___Chipping Sparrow* ___Ruffed
    [Show full text]
  • Status and Seasonal Occurrence of Birds in Dhaka University Campus
    Dhaka Univ. J. Biol. Sci. 25(1): 27‐37, 2016 (January) STATUS AND SEASONAL OCCURRENCE OF BIRDS IN DHAKA UNIVERSITY CAMPUS MST. FARHANA ARZUMAN BANU, MUNTASIR AKASH, GAWSIA WAHIDUNNESSA CHOWDHURY* AND MD. ANWAR HOSSAIN Department of Zoology, University of Dhaka, Dhaka 1000, Bangladesh Key words: Birds, Status, Seasonal occurrence Abstract A study was conducted on the status and seasonal occurrence of the birds in Dhaka University campus, from July, 2013 to February, 2014. During the study period, 54 species of birds belonging to 10 orders, 27 families and 47 genera were recorded. Of the recorded species of birds, 10 (19%) species were found as migrants and 44 (81%) as residents. Out of total species, 14 (26%) were identified as very common, 7 (13%) common, 10 (19%) uncommon, and 23 (43%) as rare. Of the resident species, 14 (25%) were very common residents, 26 (48%) common residents, 3 (6%) uncommon residents, 1 (2%) was rare resident and of the migrants, 7 (13%) were common winter visitors and 3 (6%) were found as uncommon winter visitors. From the study site, 28 (52%) species of passerine birds were observed and remaining 26 (48%) were non‐passerines. The highest number of birds was recorded in dry period/winter season (November ‐ February) and the lowest in wet period/monsoon (July ‐ October). Introduction Bird is a group of warm‐blooded, egg‐laying vertebrates of the class Aves having its body covered with feathers and forelimbs modified into wings(1,2). They have relatively large brain, keen sight and acute hearing, but little sense of smell. They share a common ancestry with reptiles and are believed to be evolved on the earth more than 150 million years ago(2‐4).
    [Show full text]
  • A New Subspecies of Eurasian Reed Warbler Acrocephalus Scirpaceus in Egypt
    Jens Hering et al. 101 Bull. B.O.C. 2016 136(2) A new subspecies of Eurasian Reed Warbler Acrocephalus scirpaceus in Egypt by Jens Hering, Hans Winkler & Frank D. Steinheimer Received 4 December 2015 Summary.—A new subspecies of European Reed Warbler Acrocephalus scirpaceus is described from the Egypt / Libya border region in the northern Sahara. Intensive studies revealed the new form to be clearly diagnosable within the Eurasian / African Reed Warbler superspecies, especially in biometrics, habitat, breeding biology and behaviour. The range of this sedentary form lies entirely below sea level, in the large depressions of the eastern Libyan Desert, in Qattara, Siwa, Sitra and Al Jaghbub. The most important field characters are the short wings and tarsi, which are significantly different from closely related A. s. scirpaceus, A. s. fuscus and A. s. avicenniae, less so from A. baeticatus cinnamomeus, which is more clearly separated by behaviour / nest sites and toe length. Molecular genetic analyses determined that uncorrected distances to A. s. scirpaceus are 1.0–1.3%, to avicenniae 1.1–1.5% and to fuscus 0.3–1.2%. The song is similar to that of other Eurasian Reed Warbler taxa as well as that of African Reed Warbler A. baeticatus, but the succession of individual elements appears slower than in A. s. scirpaceus and therefore shows more resemblance to A. s. avicenniae. Among the new subspecies’ unique traits are that its preferred breeding habitat in the Siwa Oasis complex, besides stands of reed, is date palms and olive trees. A breeding density of 107 territories per 10 ha was recorded in the cultivated area.
    [Show full text]