4. UNUSUAL EXPERIENCES WITH BIRDS

Earlé, R. A. 1989. Breeding biology of the Redbreasted Swallow Hirundo semirufa. Ostrich 60: 13–21.

The two races of the Redbreasted Swallow Hirundo semirufa seem to have separate breeding seasons with the northern race H. s. gordoni breeding April-July, while most records for the nominate race fall in October-February. All nests studied were in concrete culverts less than 1 m high. Eggs laid in second clutches by individual females weighed significantly less than eggs laid in first clutches. Eggs hatched on average 16,2 days after incubation started or 18–21 days after the eggs were laid. Only females incubated. Chicks fledged 23–25 days after hatching and reached a maximum body mass of about 31,5 g on day 18 before a steady decline in mass until fledging. Most nesting failures resulted from infertile eggs or starvation of young in the nest (16,2% of all young starved). Overall breeding success was 60,6%. In all, 81,8% of first clutches produced fledglings but only 44,4% of second clutches. Over a three year period 4,9 young were produced per pair breeding in the area (1,6 young/pair/breeding season).     

Water repellency and feather structure of the Blue Swallow Hirundo atrocaerulea

Rijke, A.M., Jesser, W.A., Evans, S.W & Bouwman, H. 2000. Water repellency and feather structure of the Blue Swallow Hirundo atrocaerulea. Ostrich 71 (1 & 2): 143–145.

The Blue Swallow is an endangered species in southern Africa and is probably the most endangered passerine. It is restricted to escarpments with grasslands above 1 000 m where mists are frequent. It appears to forage on the wing even in thick mist raising the question of feather wettability in relation to its adaptation. Extensive physical and behaviourial adaptations are known to occur in a wide variety of birds to deal with the problem of shedding water continuously. To study the water repellency and resistance to water penetration of Blue Swallow feathers, we have examined the microscopic structure of head, back, throat, breast and abdominal feathers as well as remiges and tail feathers by transmission light microscopy. The width (2R) and separation (2D) of rami and barbules have been measured and were used to calculate the parameter (R + D)/R that serves as an indicator ofwater shedding potential. For the remiges and tail feathers the values of the (R+D)/R range from 5 to 10 which is comparable to values for other terrestrial birds. However, for body feathers the range is from 10 (head) and 35 (abdomen)-higher than previously observed for any other bird including Swifts, Apodidae. Blue Swallow feathers are thus the most effective feather yet discovered at repelling water drops. The water repellency is highest in those feathers that are relatively shielded From the direct impact of small water drops (throat, breast, abdomen, back). By contrast, the flight feathers must possess a relatively large resistance to water penetration to avoid becoming waterlogged and this is coupled to low (R+D)/R values. Values for the barbules lay between 2 and 6—the same as found for other bird families—supporting an earlier conclusion that they have little direct effect in repelling water.     

SOME OBSERVATIONS ON THE DIDRIC CUCKOO

Earlé R. A. 1986. The breeding biology of the South African Cliff Swallow. Ostrich 57: 138–156.

The South African Cliff Swallow Hirundo spilodera breeds in dense colonies usually under man-made concrete bridges. The clutch size is 1–4 eggs but most 4-egg clutches are probably the result of conspecific brood parasitism. The incubation period averages 14,6 days and the fledling period 24,1 days. Although only the female Cliff Swallow has a featherless brood-patch, both males and females incubate effectively. Nestlings reach a maximum weight of up to 31 g between 19 and 22 days, about 10 g more than average adult weights. This weight increase of nestlings is mostly the result of an increase in water content of the body. Both parents feed the chicks, with the highest rate of feeding during the midday hours. In all, 56% of all eggs laid produced flying young, with a recruitment rate of 0,9 young: 1 adult per season.     

The influence of mist and rain on the reproductive success of the Blue Swallow Hirundo atrocaerulea (1995–96)

Evans, S.W. & Bouwman, H. 2000. The influence of mist and rain on the reproductive success of the Blue Swallow Hirundo atrocaerulea. Ostrich 71 (1 & 2): 83–86.

Due to the locality of the Blue Swallow Natural Heritage Site it appears that the birds have no alternative but to forage in the mist. The birds cease foraging as soon as it starts raining. Eight eggs failed to hatch after a week in which rainfall occurred for 60% and mist for 85% of the time. Later in the season a further six eggs failed to hatch after a week in which rainfall occurred for 18% and mist occurred for 65% of the time. The only mortality of two nestling Blue Swallows occurred at the end of a week in which rainfall occurred for 65% and mist was recorded for 85% of the time. At a nest containing three eggs, during the presence of mist (16°C wet/19°C dry) the female Blue Swallow spent a mean of 52 min h^?1 foraging and therefore only a mean of 8 min h^?1 incubating. In the absence of mist (21°C wet/26°C dry) the female Blue Swallow spent a mean of 25 min h^?1 foraging and therefore 35 min h^?1 incubating. Rainfall did not occur during the monitoring of this nest. It appears that the mist greatly reduces the foraging efficiency of the birds and that rainfall duration impacts on the birds by limiting the available foraging time.     

DISTRIBUTION,MIGRATION AND TIMING OF MOULT IN THE SOUTH AFRICAN CLIFF SWALLOW

Earle, R. A. 1987. Distribution, migration and timing of moult in the South African Cliff Swallow. Ostrich 58:118-121. The South African Cliff Swallow Hirundo spilodera breeds in South Africa mainly between 25 and 31S and 24 and 31E. In some years with exceptionally high rainfall the breeding range is more extensive. Man has probably had a pronounced influence on the present-day distribution of this species. Seven winter recovery/collecting localities are known from the lower Congo basin in Zaire. Possible migrating birds were observed in Zambia and Malawi in the east, and on the Namibian coast in the west. The few sight records suggest a direct migrational route over Botswana. Moult takes place between March and September primarily in the winter quarters, but about 2% of the birds handled during March and April started moult before migrating.     

SOME RESULTS OF BIRD-BANDING IN THE CONGO (KINSHASA)

The global Blue Swallow Hirundo atrocaerulea was classified as Vulnerable in 2010 on account of its small and rapidly declining population estimated at less than 1 500 pairs. We undertook this study to gain a better understanding of the current status and threats facing this migratory species. Three previously unknown areas that might be part of the species' non-breeding range were identified in Kenya and northern Tanzania. Within its breeding range we identified three previously unknown areas of potentially suitable habitat, one in Tanzania and two in Malawi, which require further exploration. Population viability assessment predicted that the Blue Swallow population will decline by 8% in 10 years. The overall probability of extinction of the species in the wild is 3%. Minimum viable population size analysis suggests that a goal for the long-term conservation of the Blue Swallow should be to mitigate current threats that are driving declines such that the population increases to a minimum of 3 600 individuals. This should consist of at least 900 individuals in each of the four clusters identified, along with a minimum of 500 individuals in at least one of the meta-populations per cluster. The four clusters are located in (1) the southeasten Democratic Republic of the Congo, (2) highlands of southern Tanzania and northern Malawi, (3) eastern highlands of Zimbabwe and (4) South Africa and Swaziland. The current proportions of the Blue Swallow population in strictly protected and unprotected areas on their breeding grounds are 53% and 47%, respectively, whereas on their non-breeding grounds the corresponding percentages are 25% and 75%, respectively. Our reassessment of the Blue Swallow's risk of extinction indicates that it continues to qualify as Vulnerable according to the IUCN/SSC criteria C2a(i).     

Field test of an automated radio‐telemetry system: tracking local space use of aerial insectivores

Documenting local space use of birds that move rapidly, but are too small to carry GPS tags, such as swallows and swifts, can be challenging. For these species, tracking methods such as manual radio‐telemetry and visual observation are either inadequate or labor‐ and time‐intensive. Another option is use of an automated telemetry system, but equipment for such systems can be costly when many receivers are used. Our objective, therefore, was to determine if an automated radio‐telemetry system, consisting of just two receivers, could provide an alternative to manual tracking for gathering data on local space use of six individuals of three species of aerial insectivores, including one Cliff Swallow (Petrochelidon pyrrhonota), one Eastern Phoebe (Sayornis phoebe), and four Barn Swallows (Hirundo rustica). We established automated radio‐telemetry systems at three sites near the city of Peterborough in eastern Ontario, Canada, from May to August 2015. We evaluated the location error of our two‐receiver system using data from moving and stationary test transmitters at known locations, and used telemetry data from the aerial insectivores as a test of the system's ability to track rapidly moving birds under field conditions. Median location error was ~250 m for automated telemetry test locations after filtering. More than 90% of estimated locations had large location errors and were removed from analysis, including all locations > 1 km from receiver stations. Our automated telemetry receivers recorded 17,634 detections of the six radio‐tagged birds. However, filtering removed an average of 89% of bird location estimates, leaving only the Cliff Swallow with enough locations for analysis of space use. Our results demonstrate that a minimal automated radio‐telemetry system can be used to assess local space use by small, highly mobile birds, but the resolution of the data collected using only two receiver stations was coarse and had a limited range. To improve both location accuracy and increase the percentage of usable location estimates collected, we suggest that, in future studies, investigators use receivers that simultaneously record signals detected by all antennas, and use of a minimum of three receiver stations with more antennas at each station.     

Sexual dimorphism in wing and tail length as shown by the Swallow Hirundo rustica

In both sexes of Hirundo rustica two metric traits are significantly different. One of these traits, tail length, shows a positive correlation between mates and a negative correlation with the date of first egg laying. On the other hand, wing lengths are not significantly related in any of the corresponding tests. Similar relations were recorded both for all analysed birds and for at least two-year-old individuals. It is suggested that sexual selection, as proposed by Darwin (1871) for monogamous birds, is responsible for sexual dimorphism in the tail length of the Swallow. It seems that intersexual difference in wing length could be a result of such mechanisms as stabilizing the body sizes of males and females at different energetically optimum levels by natural selection.     

Long‐term changes in the migration phenology of UK breeding birds detected by large‐scale citizen science recording schemes

The timing of migration is one of the key life‐history parameters of migratory birds. It is expected to be under strong selection, to be sensitive to changing environmental conditions and to have implications for population dynamics. However, most phenological studies do not describe arrival and departure phenologies for a species in a way that is robust to potential biases, or that can be clearly related to breeding populations. This hampers our ability to understand more fully how climate change may affect species’ migratory strategies, their life histories and ultimately their population dynamics. Using generalized additive models (GAMs) and extensive large‐scale data collected in the UK over a 40‐year period, we present standardized measures of migration phenology for common migratory birds, and examine how the phenology of bird migration has changed in the UK since the 1960s. Arrival dates for 11 of 14 common migrants became significantly earlier, with six species advancing their arrival by more than 10 days. These comprised two species, Blackcap Sylvia atricapilla and Chiffchaff Phylloscopus collybita, which winter closest to Britain in southern Europe and the arid northern zone of Africa, Common Redstart Phoenicurus phoenicurus, which winters in the arid zone, and three hirundines (Sand Martin Riparia riparia, House Martin Delichon urbicum and Barn Swallow Hirundo rustica), which winter in different parts of Africa. Concurrently, departure dates became significantly later for four of the 14 species and included species that winter in southern Europe (Blackcap and Chiffchaff) and in humid zones of Africa (Garden Warbler Sylvia borin and Whinchat Saxicola rubetra). Common Swift Apus apus was the exception in departing significantly earlier. The net result of earlier arrival and later departure for most species was that length of stay has become significantly longer for nine of the 14 species. Species that have advanced their timing of arrival showed the most positive trends in abundance, in accordance with previous studies. Related in part to earlier arrival and the relationship above, we also show that species extending their stay in Great Britain have shown the most positive trends. Further applications of our modelling approach will provide opportunities for more robust tests of relationships between phenological change and population dynamics than have been possible previously.     

CHAIRMAN'S REPOST, 1954–55

Brown, C. R. 1986. Feather growth, mass loss and duration of moult in Macaroni and Rockhopper Penguins. Ostrich 57:180-184.

The development of new feathers, loss of body mass and the duration of moult were investigated in Macaroni Penguins Eudyptes chrysolophus and Rockhopper Penguins E. chrysocome at Marion Island, southern Indian Ocean. New feathers began developing under the skin before the birds returned ashore to moult, and only began protruding through the skin about five days later when they were already over half their final length. Feather synthesis was complete by 21 days after the birds returned ashore. Loss of body mass was similar to previous observations for the species, but previous reports on the duration of moult do not take into account that moult begins while the birds are still at sea.     

Migrant European Swallows Hirundo rustica in southern Africa: a southern perspective

Oatley, T.B. 2000. Migrant European swallows Hirundo rustica in southern Africa: a southern perspective. Ostrich 71 (1 & 2): 205–209.

A total of 1 457 recoveries and controls of European Swallows Hirundo rustica in the South African Bird Ringing Unit data bank were analysed to provide an update of the apparent origins and dispersion of migrant European Swallows in southern Africa, to investigate local movements within southern Africa, and to yield an estimate of the age structure of the visiting migrants. Although birds from the former USSR and from Britain and Ireland predominate, over 200 recoveries from 20 other European countries have been recorded. More than half of the swallows migrating to southern Africa are from the central third of the species' breeding range. The dispersion of recoveries of swallows ringed in Britain and Ireland is widespread, with 55% recorded from the Eastern Cape, Free State and KwaZulu-Natal. Controls of southern African-ringed swallows at roosts and recoveries elsewhere in the subcontinent suggest that the daily range of migrant swallows is encompassed within a circle of 100 km diameter, but wide-ranging intra-seasonal movements within South Africa have also been recorded. Conservative estimates of the age of European Swallows at recovery indicate that as many as 14% of migrant swallows ringed in southern Africa may Survive to more than three years of age. It is suggested that the experience of migrants that survive to return to Africa one or more times may permit some flexibility in choice of final destination and that mixing of populations in roosts may result in birds arriving at new destinations.     

The timing of breeding and moult of the Lesser Striped Swallow Hirundo abyssinica

The Lesser Striped Swallow seems to have two different breeding populations. The birds south of 10°s breed largely during the spring and summer (July to April) and moult from about April to August. Birds further north breed throughout the year, but mainly during the first seven months of the year. Moult in the birds north of 10°s is from July to February when few birds are breeding. There seem to be two clearly defined moulting populations, with the southern breeding population moulting largely south of 10°s and the east African breeding population moulting largely north of the equator. In both populationsmoult and breeding seem to be separated in time, at least at the individual level.     

MINUTES OF THE ANNUAL GENERAL MEETING OF THE SOUTH AFRICAN ORNITHOLOGICAL SOCIETY,HELD AT CAPE TOWN, 26 JUNE 1959

Brown, C. J. 1989. Plumages and measurements of the Bearded Vulture in southern Africa. Ostrich 60: 165–171.

Four different age classes of the southern African Bearded Vulture Gypaetus barbatus are recognized and their plumages described: juvenile (3–24 months old), immature (24–45 months), subadult (45–60 months) and adult (60+ months). There was no significant difference in size between adult male and female birds. Adults were larger than juvenile birds in bill width, beard length, wingspan and mass, and had a higher aspect ratio and wing loading, while juvenile birds were larger than adults in the length of their outer rectrices, tail area, wing breadth and wing area. These features are considered to be adaptive to young birds inexperienced in flying. Immature and subadult birds were intermediate in size between juveniles and adults. Bearded Vultures differ from other large raptors in two sets of physical characteristics, (a) those adapted to cold, mountainous habitat, e.g. feathered head and face, unusually long wings, a high aspect ratio and a particularly long tail, and (b) those adapted to their diet of mainly bones, e.g. wide gape, beard and relatively long talons for carrying food.     

The timing of breeding and moult of the Lesser Striped Swallow Hirundo abyssinica

The Lesser Striped Swallow seems to have two different breeding populations. The birds south of 10°S breed largely during the spring and summer (July to April) and moult from about April to August. Birds further north breed throughout the year, but mainly during the first seven months of the year. Moult in the birds north of 10°S is from July to February when few birds are breeding. There seem to be two clearly defined moulting populations, with the southern breeding population moulting largely south of 10°S and the east African breeding population moulting largely north of the equator. In both populations moult and breeding seem to be separated in time, at least at the individual level.     

6. NESTING OF NYASA VIOLET-BACKED SUNBIRD ON ELVINGTON FARM,BEATRICE DISTRICT,SOUTHERN RHODESIA

Summary

Summers, R. W., Underhill, L. G, Waltner, M. &; Whitelaw, D. A. 1987. Population, biometrics and movements of the Sanderling Calidris alba in southern Africa. Ostrich 58:24-39.

The Sanderling in southern Africa is restricted to coastal habitats. The population during the austral summer was estimated to be 78000. Highest densities occurred along the west coast where the Benguela Up-welling System gives rise to enriched inter-tidal invertebrate communities, partly through the stranding of large kelps. Immigration from the breeding areas took place during September and November. Numbers were highest during mid summer and emigration took place in April. The summer population at Lange-baan Lagoon was biased towards males (72%). The percentage of first-year birds in the summer population fluctuated on a three-year cycle, coinciding with the lemming cycle in the Taimyr Peninsula in Siberia. It is suggested that the cyclic fluctuation is caused by Arctic Foxes, and perhaps other predators, feeding on lemmings in years of lemming abundance but subsisting on the eggs and chicks of birds when lemmings are scarce. First-year birds are similar in size (similar bill lengths) to older birds, but are lighter in mass during the summer. First-year birds do not accumulate the large fat reserves which older birds deposit between March and early May for northward migration. However, not all first-year birds remain in southern Africa. Trie 13000 km northward migration is completed within seven weeks and probably involves three long flights and two periods of replenishing fat reserves. Birds cross the Sahara to the Mediterranean, and also pass through the Caspian Sea to Siberia or through the North Sea coasts to either Siberia or Greenland. Return routes also involve the North, Caspian and Black Seas but there is little information about routes through Africa.     

家燕和金腰燕的卵胚胎心率比较

胚胎心率是衡量胚胎新陈代谢速率的重要指标。鸟类的胚胎心率随新陈代谢的增加而呈上升趋势。对早成性鸟类的种间比较发现,胚胎心率平均值随卵重量的增大而减小,卵体积小的种类具有相对较高的胚胎心率。国内有关野生鸟类胚胎心率的研究较少。2014年5~8月,在黑龙江扎龙国家级自然保护区,利用红外胚胎心率测量仪对两种近缘鸟类家燕(Hirundo rustica,n=14)和金腰燕(Cecropis daurica,n=14)的卵胚胎心率及其变化进行了测量与比较。两种燕均在孵卵的第2天开始出现胚胎心率,并随胚龄增加心率呈上升趋势,但在第8天及第11~14天家燕的胚胎心率显著低于金腰燕(第8天:z=﹣2.602,P=0.009;第11天:z=﹣2.497,P=0.013;第12天:z=﹣2.354,P=0.019;第13天:z=3.424,P=0.001;第14天:z=﹣3.380,P=0.001)。家燕卵胚胎日均增长心率(19.0±3.1)次/min,金腰燕卵胚胎日均增长心率(16.1±3.4)次/min,二者差异不显著(z=﹣1.792,P=0.073)。两种燕的胚胎心率与卵容量和卵重均不存在显著相关性[家燕:卵容量(1.73±0.09)cm3,r=0.192,P=0.511;卵重(1.74±0.09)g,r=0.128,P=0.663。金腰燕:卵容量(1.74±0.08)cm3,r=0.040,P=0.891;卵重(1.51±0.09)g,r=0.054,P=0.855]。这可能表明,卵大小和卵重量对家燕与金腰燕的胚胎心率均影响不明显。     

A review of the threats to adult survival for swallows (Family: Hirundinidae)

Capsule: For declining migratory birds, including many aerial insectivores, such as swallows, there is evidence that adult survival is a demographic process with strong effects on population trends.

Aims: The aim was to identify and quantify the effect of threats affecting adult survival and potentially driving population declines for five well-studied swallow species: Barn Swallow Hirundo rustica, Cliff Swallow Petrochelidon pyrrhonota, Tree Swallow Tachycineta bicolor, Sand Martin Riparia riparia, and Purple Martin Progne subis.

Methods: We reviewed the literature to identify the threats to adult survival, quantified the magnitude of the effect and identified whether threats had a direct or indirect effect on survival.

Results: We identified habitat change, weather, competition, incidental loss, contaminants, insect availability, disease, and predation as threats to adult survival in swallows, although for many of these threats there was limited information to quantify their impact. However, weather, particularly cold snaps and precipitation, had negative effects on survival for many populations of four species, either directly or indirectly through effects on insect availability. When there was a relationship, weather was associated with a 13–53% decrease in survival.

Conclusion: Based on the available research, weather conditions throughout the annual cycle is a key threat to adult survival for several swallow species. However, future research on the threats to these species should consider examining the effect of insect availability and the effect of threats during the non-breeding period on survival. Finally, we suggest that new research should be devoted to understanding the importance of adult survival for declining bird populations.     

A CONVENIENT METHOD FOR RECORDING AND PROCESSING FIELD DATA

Brooke, R. K. 1984. A history of the Redeyed Dove in the southwestern Cape Province, South Africa. Ostrich 55:12-16.

At present the Redeyed Dove occurs throughout the southwestern Cape although more sparsely in the arid northwest. The literature is confused on whether the Redeyed Dove Streptopelia semitorquata has always existed in the southwestern Cape, has immigrated from the southern or eastern Cape or was introduced to the area in 1933 at Elgin from stock bred up from an importation from Beira, Moçambique. Evidence is presented that it has always been present in the southwestern Cape. The birds introduced near Elgin came from a short-winged, richly coloured population of nominate semitorquata whereas the indigenous birds belong to the long-winged, pallid australis. Specimens shot in the 1940s and 1950s show the characteristics of a hybrid swarm between the two races and more recent data suggest that this condition persists.     

Codominant PCR-based markers and candidate genes for powdery mildew resistance in melon (<Emphasis Type="Italic">Cucumis melo</Emphasis> L.)

Powdery mildew caused by Podosphaera xanthii is a major disease in melon crops, and races 1, 2, and 5 of this fungus are those that occur most frequently in southern Europe. The genotype TGR-1551 bears a dominant gene that provides resistance to these three races of P. xanthii. By combining bulked segregant analysis and amplified fragment length polymorphisms (AFLP), we identified eight markers linked to this dominant gene. Cloning and sequencing of the selected AFLP fragments allowed the development of six codominant PCR-based markers which mapped on the linkage group (LG) V. Sequence analysis of these markers led to the identification of two resistance-like genes, MRGH5 and MRGH63, belonging to the nucleotide binding site (NBS)-leucine-rich repeat (LRR) gene family. Quantitative trait loci (QTL) analysis detected two QTLs, Pm-R1-2 and Pm-R5, the former significantly associated with the resistance to races 1 and 2 (LOD score of 26.5 and 33.3; 53.6 and 61.9% of phenotypic variation, respectively), and the latter with resistance to race 5 (LOD score of 36.8; 65.5% of phenotypic variation), which have been found to be colocalized with the MRGH5 and MRGH63 genes, respectively. The results suggest that the cluster of NBS-LRR genes identified in LG V harbours candidate genes for resistance to races 1, 2, and 5 of P. xanthii. The evaluation of other resistant germplasm showed that the codominant markers here reported are also linked to the Pm-w resistance gene carried by the accession ‘WMR-29’ proving their usefulness as genotyping tools in melon breeding programmes.     

Effect of neighbour visibility on nest attendance patterns of Barn Swallows Hirundo rustica in loose colonies

To assess the benefits of nesting at a site hidden from neighbours in a loosely colonial species, the Barn Swallow Hirundo rustica, we carried out two field experiments, obstruction removal and mirror placement, both replicating a situation in which a nest is made visible from another nest. Under manipulated conditions in both experiments, females increased the length of time they stayed at their nests during the egg‐laying and late incubation stages, while males extended their duration of stay during the egg‐laying and early nestling stages in mirror placement experiments only. The results suggest that Barn Swallows conceal their nests to reduce fitness costs imposed by neighbours nesting in view and that hiding the nest can reduce the amount of time spent guarding the nest during certain stages of the breeding period.