BREEDING BIOLOGY OF THE BATELEUR

Watson, R. T. 1990. Breeding biology of the Bateleur. Ostrich 61: 13–23.

Observations were made on the breeding biology of the Bateleur Terathpoius ecaudataus between 1981 and 1984, in the central region of the Kruger Nabonal Park. Nests were uniformly distributed with a mean inter-nest distance of 5,1 km and density of 3,1 nests/100km². Single-egg clutches were laid from January to June, and laying appeared to be suressed by unusually high rainfall events. The mean productivity was 0,47 young per pair per year, an a breeding failures were mainly due to failure to lay or predation. Breeding adults chaned nest sites within their territory on average once every 2,8 years, but territories and pairs were stable from year to year. Both members of a pair put equal time into care of the young.     

POPULATION,DIET AND THE ANNUAL CYCLE OF THE LAUGHING DOVE AT BARBERSPAN,PART 4. BREEDING DATA AND POPULATION ESTLMATES

Dean, W. R. J. 1980. Population, diet and the annual cycle of the Laughing Dove at Barber-span, Part 4: Breeding data and population estimates. Ostrich 51:80-91.

From 1974–1976, Laughing Doves Streptopelia senegalensis raised an observed total of 436 young in 619 nest attempts, giving a breeding success of 0,70 young per pair nest attempt, or an overall success of 0,35 young per egg. Breeding success, estimated by computing the probability of survival of an egg through the incubation period, and of a chick through the nestling period suggest that the breeding success is about 0,33 young per egg. Nests were found in every month of the year, though there was a tendency for breeding to be concentrated during the late rainy season and the dry season. The mean annual population size of the Laughing Dove in the study area was estimated at 221 adults and juveniles by one method and at 237 adults and juveniles by another method. The number of young produced each year is correlated with the estimated population size for each year.     

Demography of the Seychelles Black Paradise-flycatcher: considerations for conservation and reintroduction

The Seychelles Black Paradise-flycatcher Terpsiphone corvina is currently listed as Critically Endangered, on the basis of small population and restricted range. Currently, there is only one self-sustaining population comprising c. 150–200 individuals on the 10km² island of La Digue (Republic of Seychelles, western Indian Ocean), and consequently the creation of additional island populations has been identified as essential to improve its conservation status. We quantified the annual breeding success, adult mortality and juvenile recruitment of the flycatcher on La Digue, monitored tri-weekly over a two-year period (June 1999–June 2001), to determine factors affecting population demographics and assess the implications for the reintroduction of populations to other islands. A total of 267 breeding attempts were recorded with c. 45% of the documented world population of pairs systematically monitored each year. On average, pairs attempted to breed three times in a 12-month period (range 0–6), although not all attempts were successful. Breeding success was consistently low between years: 62% of nests (controlling for observation time) and 17–19% of study territories failed to produce any fledglings in each respective 12-month period. Daily failure rates were generally higher during incubation than in the nestling period. Nests close to the forest edge were more likely to fail. The majority (143) of the 152 failed nesting attempts were consistent with depredation and were characterised by the disappearance of nest contents and sometimes by egg and chick remains and the disappearance of the adult female. Predators were identified at 13 nests: five (3.3%) were depredated by birds, and eight (5.2%) were depredated by mammals and/or reptiles: Rattus sp. were confirmed as predators. Video monitoring conducted at 14 nests also confirmed the endemic Seychelles bulbul Hypsipetes crassirostris as a nest predator. Adult mortality was c. 21% and alien predators (Rattus sp. and Felis cattus) were identified in causing adult mortality. However, in the majority of cases, reasons for adult mortality were unknown. Of the 52 marked fledglings that could have been recruited to the plateau population, 45% (23) were observed away from their natal territory c. 9–10 months after fledging, 25% (13) of which were confirmed as territory-holding individuals. We present a simple model to predict population growth using the above data, and discuss implications for the creation of additional self-sustaining populations on suitable islands.     

ASPECTS OF THE BIOLOGY OF THE FOREST BUZZARD

Palmer, N. G., Norton, P. M. & Robertson, A. S. 1985. Aspects of the biology of the Forest Buzzard, Ostrich 56: 67–73.

Aspects of the biology of the Forest Buzzard Buteo oreophilus in the southern Cape Province were studied. Information was obtained from eight nests, one of which was visited several times during the nesting period, and from a hand-reared free-living bird. Details of nest structure and locality, egg measurements, hatching period (late October to early December), nestling period (50 days ± 5 days), food intake, growth rate and development are given. Probable Cainism was observed at one nest; prey remains collected from this nest included rodents, moles, birds, snakes and insects. The use of pine trees for nesting is discussed.     

Nestbox provisioning in a rural population of Eurasian Kestrels: breeding performance,nest predation and parasitism

The breeding biology of the Eurasian Kestrel Falco tinnunculusin nestboxes in farmland was studied to test for differences between artificial and natural sites. We report on the direct effect of nestbox provisioning on some life-history traits and how nestbox use affects nest predation and parasitism. Five types of nest-sites were available: nestboxes on poles and trees (artificial sites), stick nests on trees, stick nests on pylons and holes in buildings (‘natural’ sites). The Kestrel population increased from 23 pairs in 1993 (prior to nestbox installation) to 55 in 1998 as nestboxes were provided. In general, pairs breeding in trees started to lay later than those nesting in nestboxes on poles or in building holes, but this difference was probably associated with habitat quality rather than nest type. Differences in clutch size were found between nest-sites in some years, and were associated with laying date and, probably, with variation in territory quality. Using only data from successful nests, pairs breeding in nestboxes produce more fledglings than those in building holes or pylons. The frequency of nest predation was higher in natural sites than in nestboxes. The number of fledglings from pairs breeding in nestboxes was higher than from those breeding in old stick nests in trees when all nests were considered. Nestbox provisioning had no effect on the occurrence of the ectoparasite Carnus hemapterus, but chicks from nestboxes showed higher intensity of infection. Our results suggest that nestbox provisioning increases reproductive success and the frequency of nest predation or intensity of parasite infestation in Kestrels.     

BREEDING NOTES ON THE BLACK-NECKED GREBE PODICEPS NIGRICOLLIS BREHM

Summary

Tarboton, W. R. &; Fry, C. H. 1986. Breeding and other behaviour of the Lesser Jacana. Ostrich 57: 233–243.

Breeding Lesser Jacanas were studied briefly at Lake St Lucia (Zululand), Hwange (Zimbabwe) and the Okavango Delta (Botswana). The species is monogamous and breeding birds are dispersed as territorial pairs. Male and female share incubation nearly equally, alternating at the nest in shifts averaging 39min; the eggs are attended (incubated or shaded), on average, for 82% of the daylight hours. Eggs are incubated by holding them against the breast with the underside of the wings; at least one chick was seen carried under a parent's wing. The pullus, foraging behaviour, courtship and vocalisations are described. It is suggested that the Lesser Jacana's small egg necessitates a high rate of nest attendance which could account for the sociosexual differences between this species and other jacanas.     

Spatial and temporal variation in breeding parameters of two south-temperate populations of House Wrens

Studies of variation in breeding parameters are often based on temporal analyses of a single population. However, to differentiate between the effects of regional and local factors, neighboring populations with limited interpopulational dispersal need to be compared. We studied two nearby (< 5 km apart) populations of House Wrens (Troglodytes aedon bonariae) at two ranches (Los Zorzales, 10 years; La Esperanza, 13 years) in south-temperate Argentina to assess the possible effects of regional and local factors on breeding phenology. For each breeding season, we recorded laying dates, clutch sizes, and length of the breeding season, and estimated the reproductive synchrony of first and second breeding attempts. We examined how these breeding parameters were affected by weather, population density, and rates of nest failure. With favorable temperatures during the pre-reproductive period (September–October), wrens in both populations initiated first breeding attempts earlier. However, ordinal laying dates were also affected by local factors, with wrens at Los Zorzales initiating breeding attempts earlier than those at La Esperanza. We found a spatial correlation in clutch sizes between populations for the 2007–2012 breeding seasons, but clutch sizes of first and second nesting attempts showed low variability. Reproductive synchrony of first nesting attempts varied among years, suggesting an effect of regional factors. However, we detected no synchronization between populations and were unable to identify environmental variables that explained the temporal variation. Ordinal laying dates of second clutches were strongly correlated with the ordinal laying dates of first clutches. We also found that the length of breeding seasons was longer when daily nest mortality rates were lower. Although environmental factors seemed to affect the decision of when to start breeding, pairs with successful first nesting attempts were more likely to initiate second nests, thus affecting the length of the breeding season. The spatial variation and temporal variation of the breeding parameters of House Wrens in our study provide evidence of marked plasticity in their breeding decisions and allowed us to identify local and regional environmental factors related to this variation.     

BREEDING DENSITY AND NEST SITE CHARACTERISTICS OF THE PEREGRINE FALCON FALCO PEREGRINUS MINOR IN THE SOUTHWESTERN CAPE,SOUTH AFRICA

Pepler, D., Van Hensbergen, H.J. & Martin, R. 1991. Breeding density and nest site characteristics of the Peregrine Falcon Falco peregrinus minor in the southwestern Cape, South Africa. Ostrich: 62: 23–28.

A survey of nest sites and nest site characteristics is used to obtain an estimate of the breeding density of the Peregrine Falcon Falco peregrinus minor in the southwestern Cape, South Africa. The breeding density from a small intensively studied area around the town of Stellenbosch is extrapolated to the region. This extrapolation is justified since nest site characteristics suggest that suitable sites are widespread in the region. Lower and upper estimates of 48 and 95 pairs respectively were obtained for the area above 300 m. This gives densities of one pair per 199 km² for the lower estimate and one pair per 100 km² for the upper estimate. For the entire study area the densities are one pair per 806 km² and 407 km² respectively.     

4. ONE YEAR'S CENSUS AND STUDY OF BIRDS IN 2½ ACRES OF ALEANY BUSHVELD. (Part 2.) April, 1945, to March, 1946

Hooded Vultures Necrosyrtes monachus are critically endangered but little is known of their year-round use of nests or whether other species usurp Hooded Vulture nest sites. We investigated visitation rates by Hooded Vultures and other species (including potential nest predators and usurpers) to examine their effect on Hooded Vulture breeding success. We present observations of 33 species recorded by camera traps at 12 Hooded Vulture nests over a total of 93 nest-months (2 095 nest-days). Several pairs of Hooded Vultures visited their nests regularly during the non-breeding season, some adding nesting material, highlighting that pairs visited their nest(s) year round. Egyptian Geese Alopochen aegyptiaca, potential usurpers of raptor nests, were present at occupied and unoccupied Hooded Vulture nests, but we recorded no usurpation of nests by Egyptian Geese and they had no impact on vulture breeding success. Hooded Vulture breeding failure was linked to two species only: camera-trap imagery recorded one case of predation of a vulture egg by a Chacma Baboon Papio ursinus, and one case of a Martial Eagle Polemaetus bellicosus predating a vulture nestling. We recommend expanding the Hooded Vulture nest monitoring programme to include more pairs.     

The breeding biology and causes of nest failure of Scottish Black-throated Divers Gavia arctica

The breeding biology and causes of nest failure were examined for Black-throated Divers Gavia arctica in core areas of their Scottish breeding range in 1983–1987. Breeding was confirmed for up to 88% of territorial pairs each year ( n = 28–62), and 76% of nests were on islands. Hatching success was consistently low with, on average, only 43% of territorial pairs managing to hatch a clutch each year; 64% of recorded nest failures occurred during the first week of the 4-week incubation period.
Overall breeding success in West Sutherland in 1984–1987 averaged 0.23 chicks per territorial pair per year, while in Ross-shire for 1986–1987 it was 0.29. Forty percent of hatched chicks survived to fledge, and 92% of recorded deaths occurred in the first fortnight after hatching; 4.8% of fledged broods held two chicks.
Causes of nest failure were assessed with the aid of surveillance cameras. Approximately 30% of losses were due to water level changes (mostly floods), 48% to predators (primarily nocturnal mammals, but also Hooded Crows Corvus corone ), 13% to human egg collectors and 5% to desertion following human disturbance.
Scottish Black-throated Divers produce only half the number of chicks tentatively estimated to be required to maintain a stable population. The main difference between the Scottish and more successful Swedish populations is in the degree of chick mortality.     

THE BREEDING BIOLOGY OF THE BLACK-BELLIED STORM-PETREL FREGETTA TROPICA

The breeding cycie and habits of the Black-bellied Storm-petrel are described from observations made over three seasons at Signy Island, South Orkney Islands. The species is strictly nocturnal on land and nests in stable scree slopes. With an estimated population of 100–200 pairs, Fregetta tropica is the rarest petrel breeding on the island. In general, the breeding cycle of F. tropica resembles that of Oceanites oceanicus. Birds usually arrive from mid-November onward and return to the same nest and mate in successive seasons. The female is absent from the nest for a week or more before the egg is laid, during which time the male continues to visit the site. From ten laying dates, egg laying appears normally to begin during the last week in December, but evidence is given that, in 1966-67, laying was delayed by heavy winter snow build-up coupled with a late melt. The egg comprises 26 % of the body weight of the female. Incubation is by both sexes in alternate spells of three days, the whole period lasting 38–44 days. The chick is left alone in the nest by the parents almost immediately after hatching. Chick growth is described briefly and the effects of drift snow on development are discussed. The fledging periods of two chicks were 65 and 71 days, departure from the nest taking place in mid-April. Measurements of 36 Signy Island birds show considerable variability but are similar to those from other breeding localities.     

BREEDING BIOLOGY OF THE BEARDED VULTURE IN SOUTHERN AFRICA,PART I: THE PRELAYING AND INCUBATION PERIODS

Brown, C. J. 1990. Breeding biolo of the Bearded Vulture in southern Africa, Part I: The pre-laying and incubation periods. Ostrich 61: 24–32.

In southern Africa the Bearded Vulture Gpaetus barbatus lays its eggs in mid-winter. between the second half of May and the first week of July. Pairs became more active in their nesting areas about six weeks before laying and usually roosted there at night. Courtship flights were less frequent and demonstrative than in Eurasian birds and took place mainly in the late afternoons. During the pre-laying period most nest visits (77%) were to bring nesting material, 92% by the male. All nesting material was arranged by the female. Copulation was always preceded by allopreening, and occurred most frequently in the mornings. No copulation or courtship display took place after the first egg had been laid. Of 18 clutches, 16 (89%) contained two eggs and the remainder one egg. The laying interval was usually 3–5 days (range 2–9 days). Incubation started with the first egg and was evenly shared by both parents during the day, but only the female incubated at night, individual pairs maintained distinctive nest attendance and foraging period timetables, which allowed sufficient time for self-foraging by both parentes. No food was brought into the nest during the pre-laying and incubation periods, but in some pairs food was cached in nearby potholes in cliffs. The incubation period was 56–57 days.     

The breeding biology of Abdim's Stork Ciconia abdimii in the far north of Benin

Adjakpa, J.B. 2000. The breeding biology of Abdim's Stork Ciconia abdimii in the far north of Benin. Ostrich 71 (1 & 2): 61–63.

Little is known about the biology of Abdim's Stork Ciconia abdimii, in Benin. I studied the nesting of this intra- African migrant in the wet season of 1996. Breeding pairs arrived at the end of March 1996. Seven nest sites were found, involving 92 pairs; the largest colony was of 51 pairs. The storks used five different large tree species for nesting. Egg-laying began in early April and lasted until 2 July. Most clutches were of 3–4 eggs. Incubation lasted 28–29 days. A total of 196 young storks fledged (all of which were ringed), representing a success rate of 76.5% per egg laid and 86.0% per egg hatched. The last storks left the colonies on 9 September 1996, 164 days after the first ones arrived on 30 March. The species is threatened in Benin by human persecution and by widespread pesticide use: it urgently requires official protected status.     

THE BREEDING BEHAVIOUR OF THE LESSER FLAMINGO PHOENICONAIAS MINOR

This paper summarizes what has been learned about the breeding behaviour of the Lesser Flamingo Phoeniconaias minor from 1954 to 1969, especially at Lake Magadi, Kenya, in 1962. The only known regular breeding site is on soda mudflats at Lake Natron, Tanzania. Lake Magadi, used in 1962 when Lake Natron was full of water, may only have been used once this century. Breeding has been sporadically reported from other lakes, but reports are usually inadequate and in many cases successful breeding was not proven. At Lake Natron the breeding site is in the middle of the lake which is 70 km long by 24 km wide. Breeding conditions are extremely harsh, mid-day temperatures regularly exceeding 50^oC and reaching 70–75^oC. The advantage of the site lies in its complete freedom from predatory mammals. Details of known breeding, obtained by aerial surveys, are given. Lesser Flamingos do not breed annually, and tend to start in the last quarter, October to December, of any year in which they breed. There is no obvious relation between food supply and this breeding date. The last quarter of the year at Lake Natron tends to be rainy and warm. No really large-scale breeding has been observed since 1962. The methods used for estimating adults and young are given. They have shown good correlation with ground counts at Lake Magadi in 1962. The total population is of the order of three to four million, and the largest known breeding colonies were of 1,100,000 pairs at Lake Magadi in 1962 and 570,000 pairs in 1957 at Lake Natron. From 1953 to 1962 inclusive about 275,000 pairs (1/5 to 1 /6 of the population) bred annually on average, but since 1962 the average number breeding per year has been less, reducing the overall average to perhaps 180,000 pairs. At this rate a pair takes 22–24 years to replace itself. The nuptial display of the Lesser Flamingo resembles in many respects that of the Greater Flamingo Phoenicopterus ruber. When displaying, Lesser Flamingos congregate in a tightly-packed flock, rapidly moving, in which various ritual movements are performed. Display normally takes place in certain sites far from known breeding grounds, and may be stimulated by conditions of very dense population. Lesser Flamingos build mud-mound nests similar to but smaller than those of the Greater Flamingo. Measurements, weights, and other details are given. The huge 1962 Magadi colony involved the excavation of some 20,000 metric tons of soda mud. One egg is normally laid. Large numbers of birds tend to lay synchronously in particular parts of the colony. The threshold numbers for breeding may be of the order of 5,000 pairs. Both sexes incubate, for about 28–29 days. Incubating birds are liable to desert en masse when disturbed, e.g. by hyenas. 70–90% of eggs hatch, usually about 85%. Larger colonies are more successful than smaller, and birds that lay out of phase with others tend to desert without hatching. The development of the young resembles that of the Greater Flamingo, but the two are distinguishable at an early age by bill structure. At Lake Natron the fledging period is about 70 days, but at Lake Magadi it was about 90 days, probably because the parents had to fly to Lake Natron for food. Adults attend the chicks closely for the first week of life, but thereafter leave them increasingly. Chicks more than one week old gather in herds, which eventually aggregate to huge numbers, 300,000 or more. Both at Lake Natron and Lake Magadi the chicks moved en masse out of the breeding area to gathering grounds in shallow water, where they remained till able to feed themselves and fly. Both sexes feed the young with regurgigated liquid matter, delivered bill to bill with parent and young both facing forward, as in the Greater Flamingo. Feeding details were not closely observed at Lake Magadi as most feeding took place after dark. Breeding success has varied from 5 to 75%, averaging 41 to 43% of eggs laid. The 1962 Magadi colony had 33 to 38% breeding success. Mass moult to flightlessness is described. It may occur before, during, or after the breeding season, or without breeding, and normally only at Lake Natron. It lasts six to eight weeks, perhaps three weeks for an individual, and may be controllable in that it did not occur at Lake Magadi in 1962 when its effects would have been fatal for the colony. Predation by large mammals (from lions to jackals) and birds, especially Egyptian and other Vultures, is described and roughly quantified. Predation from all causes may have resulted in 5% loss at the Magadi colony, but at Lake Natron is probably less. Eight thousand young Lesser Flamingos and 80 Greater Flamingos were ringed at Lake Magadi in 1962. Ringing methods are described. Recoveries have been meagre, the most distant being from the Awash Valley, Ethiopia. No rings have been observed among the adult population in recent years. The most probable explanation of the poor results is ring loss through chemical action of the water.     

Managing ecological traps: Logging and sapsucker nest predation by bears

We tested the equal preference ecological trap hypothesis for breeding yellow-bellied sapsuckers (Sphyrapicus varius) along a time-since-harvest gradient (1–5 yr, 16–20 yr, 21–25 yr, and >60 yr) in selection system-logged hardwood forests in Algonquin Provincial Park, Ontario. Yellow-bellied sapsuckers preferred 1–5 year and >60-year-old cuts equally and more than 16–20 year and 21–25-year-old cuts. More-abundant arthropod food and/or higher-quality sap resources may have attracted yellow-bellied sapsuckers to 1–5 year and >60-year-old cuts. Only 52% of pairs raised fledglings in 1- to 5-year-old cuts during years when nest predation by American black bears (Ursus americanus) was common, the incidence of which was negatively related to increased availability of American beech (Fagus grandifolia) nuts from the previous autumn. By contrast, 88% of pairs raised fledglings in all years in >60-year-old cuts. One- to 5-year-old cuts were demographic sinks that represent equal-preference ecological traps in years when nest predation by bears was common, whereas >60-year-old cuts were always demographic sources. High-quality habitat cues for nesting yellow-bellied sapsuckers appear to be retained for 1–5 years after selection system logging but fail to deliver safe nest sites. Cavities excavated in heart-rot-infected nest trees are least likely to be depredated because cavity walls are typically harder and deter entry by depredating bears. Retaining more potential nest trees per ha at harvest (especially American beech with heart-rot) may increase the proportion of sapsucker nests that are excavated in bear-resistant trees, thereby reducing nest predation and increasing fecundity. © 2012 The Wildlife Society.     

4. A FIELD NATURALIST'S PEREGRINATIONS. BIRD NOTES FROM A NORTHERN SECTOR OF SOUTHERN RHODESIA—Part III

Boyer, H. J. 1988. Breeding biology of the Dune Lark. Ostrich 59:30-37.

The peak of the breeding season of the Dune Lark Mirafra erythrochlamys occurred in January and February and was not dependent on rainfall. Most nests were domed, although one undomed nest was recorded. Ninety-one percent of clutches were of two eggs (mean = 1,9; range 1–2; n = 11). The eggs are described and measurements given. Incubation, by the female only, began with the laying of the second egg, and hatching occurred after 13–14 days. Growth and development of nestlings are described. The young left the nest after 12–14 days, and post-nestling parental care lasted for approximately one month. Sixty-one percent of eggs hatched. and 28% produced young which successfully left the nest. Most losses of eggs and young were the result of predation.     

The breeding biology of the Scimitarbilled Woodhoopoe

Steyn, P. 1999. The breeding biology of the Scimitarbilled Woodhoopoe. Ostrich 70 (3&4): 173–178.

The breeding biology of the Scimitarbilled Woodhoopoe Rhinopomastus cyanomelas was studied at two sites in Zimbabwe over a 13-year period from 1964–1977. The pairs were resident, remained together throughout the year, and inspected their nest sites occasionally during the non-breeding season. The breeding season extended from August to December with a marked September/October peak. Eggs were laid at daily intervals. Clutch size averaged 2.9 (range 2–4). Incubation began either with the penultimate or last laid egg. During the 13–14 day incubation period the female left the nest only occasionally each day and was reliant on the male for food. This pattern continued for four days after the chicks hatch. Thereafter she started to forage and gradually increased her contribution to chick provisioning until she overtook that of the male. With one exception, he never fed the chicks directly and delivered the food to the female. The nestlings were brooded overnight for the first two weeks. The anti-predator response of the young included a malodorous brown exudation from the preen gland and unpleasant liquid excreta. The nestling period was 21–24 days and the young left the vicinity of the nest with their parents and did not return to roost in it. Twelve breeding cycles were monitored and 76% of eggs laid (n=37) produced fledged young. Second broods were raised in the same nest on two occasions after successful rearing of the first, presumably by the same pair, but the birds were not individually marked. There was no evidence of helpers at the nest.     

NOTES ON THE PEARL-BREASTED SWALLOW HIRUNDO DIMIDIATA IN THE SOUTH-WESTERN CAPE

Earlé R. A. &; Herholdt, J. J. 1988. Breeding and moult of the Anteating Chat Myrmecocichla formicivora. Ostrich 59: 155–161.

The general breeding biology and moult of the Anteating Chat Myrmecocichla formicivora was studied in open grassveld over a two-year period. During the winter (July), groups were significantly smaller than during summer (December) (1,81 ± 0,50 versus 2,85 ± 1,35 birds per group). There was a large turnover of individuals in the study area but the total population stayed the same. The breeding season in the study area lasted from September to February but analysis of nest record cards from a larger area gave a breeding season of August-April. Two types of nests were used: 90,6% were burrows in sand banks or other excavations, but 9,4%were in the mud pellet nests of Greater Striped Swallows Hirundo cucullata (n = 53). Consecutive breeding attempts were never made in the same burrow. Clutches consisted of three, four or five eggs ([Xbar] = 3,73 ± 0,67). Incubation lasted 14–14,5-15 days. The nestling period lasted 15–18 days. Fledgling/egg breeding success was 41,8% with 48,2% of all eggs not reaching the hatching stage. Juveniles showed an unequal sex ratio of 0,57 ♂ ♂: 1,0 ♀ ♀ but adults had a nearly equal ratio (0,9 ♂ ♂: 1,0 ♀ ♀). There was a significant positive correlation between the primary moult score and the week of the seven months in which moult was recorded. Juveniles underwent a complete body moult and partial primary moult 3–4 months after fledging.     

Nesting ecology of a naturalized population of Mallards Anas platyrhynchos in New Zealand

Investigating the reproductive ecology of naturalized species provides insights into the role of the source population's characteristics vs. post‐release adaptation that influence the success of introduction programmes. Introduced and naturalized Mallards Anas platyrhynchos are widely established in New Zealand (NZ), but little is known regarding their reproductive ecology. We evaluated the nesting ecology of female Mallards at two study sites in NZ (Southland and Waikato) in 2014–15. We radiotagged 241 pre‐breeding females with abdominal‐implant transmitters and measured breeding incidence, nesting chronology and re‐nesting propensity. We monitored 271 nests to evaluate nest survival, clutch and egg size, egg hatchability and partial clutch depredation. Breeding incidence averaged (mean ± se) 0.91 ± 0.03, clutch size averaged 9.9 ± 0.1 eggs, 94 ± 2% of eggs hatched in successful nests, partial depredation affected 6 ± 1% of eggs in clutches that were not fully destroyed by predators, and re‐nesting propensity following failure of nests or broods was 0.50 ± 0.003. Nesting season (first nest initiated to last nest hatched) lasted 4.5 months and mean initiation date of first detected nest attempts was 28 August ± 3.3 days. Smaller females were less likely to nest, but older, larger or better condition females nested earlier, re‐nested more often and laid larger clutches than did younger, smaller or poorer condition females. Younger females in Southland had higher nest survival; cumulative nest survival ranged from 0.25 ± 0.007 for adult females in Waikato to 0.50 ± 0.007 for yearling females in Southland. Compared with Mallards in their native range, the nesting season in NZ was longer, clutches and eggs were larger, and nest survival was generally greater. Different predators and climate, introgression with native heterospecifics and/or the sedentary nature of Mallards in NZ may have contributed to these differences.     

9. LIST OF MEMBERS (as at date of publication)

We studied the breeding ecology of the Chestnut-backed Sparrowlark Eremopterix leucotis over three years between 2008 and 2010. The breeding season was bimodal with a main peak in laying in autumn (March–April) and another smaller peak in spring (September–October). Nest microhabitat analyses showed they prefer nesting in open areas with lots of bare ground (median 67.5%). Nest entrance directions were biased towards the south (mean vector (µ) = 186.44°). The majority of nests (78.2%) had an apron at the nest entrance. The mean clutch size was 1.88 but there was geographic variation in clutch size between northern and southern races of the species. The mean incubation and nestling periods were 10.33 d (range 10–11 d) and 9.20 d (range 8–10 d), respectively. The results suggest that parental contributions during incubation are almost equal, but females made significantly more food deliveries during the nestling period compared to males. The diet of nestlings comprised mainly of invertebrates (50.2%), seeds (34.4%) and unidentified food items (15.4%). Breeding success was low, averaging 16.1% (range 8.1–20.6%), and the average number of fledged young per pair was 0.36 ± 0.71. Replacement broods were common and we also recorded repeat brooding attempts.