Non-migratory stonechats show seasonal changes in the hormonal regulation of non-seasonal territorial aggression

In many birds and mammals, male territorial aggression is modulated by elevated circulating concentrations of the steroid hormone testosterone (T) during the breeding season. However, many species are territorial also during the non-breeding season, when plasma T levels are basal. The endocrine control of non-breeding territorial aggression differs considerably between species, and previous studies on wintering birds suggest differences between migratory and resident species. We investigated the endocrine modulation of territorial aggression during the breeding and non-breeding season in a resident population of European stonechats (Saxicola torquata rubicola). We recorded the aggressive response to a simulated territorial intrusion in spring and winter. Then, we compared the territorial aggression between seasons and in an experiment in which we blocked the androgenic and estrogenic action of T. We found no difference in the aggressive response between the breeding and the non-breeding season. However, similarly to what is found in migratory stonechats, the hormonal treatment decreased aggressive behaviors in resident males in the breeding season, whereas no effects were recorded in the non-breeding season. When we compared the aggressive responses of untreated birds with those obtained from migratory populations in a previous study, we found that territorial aggression of resident males was lower than that of migratory males during the breeding season. Our results show that in a resident population of stonechats T and/or its metabolites control territorial aggression in the breeding but not in the non-breeding season. In addition, our study supports the hypothesis that migratory status does modulate the intensity of aggressive behavior.     

The status and recent breeding performance of the critically endangered Northern Bald Ibis Geronticus eremita population on the Atlantic coast of Morocco

The main wild population of the Northern Bald Ibis Geronticus eremita breeds on the Atlantic coast of Morocco in the Agadir region. This paper describes the numbers of breeding pairs over the last two decades, the recent breeding performance, the causes of egg and chick losses and their conservation implications. Since 1980 there has been no overall decline in numbers with, over the last 5 years, 59–74 pairs breeding and a peak prebreeding population of around 220 birds. In contrast with the now extinct Northern Bald Ibis populations in Turkey and elsewhere in Morocco, the birds are present in the Agadir region throughout the year and do not appear to migrate from the area outside the breeding season. Breeding performance is highly variable from one year to the next but does not appear to be related to rainfall in the vicinity of the colonies as has been reported elsewhere. It is suggested that coastal fogs in this region may buffer the adverse impacts of low rainfall and may in part account for the year-round residency of the birds. The main causes of breeding failures have been loss of eggs to predators and, most importantly, poor chick survival as a result of starvation and predation. Conservation action to date has focused on reducing the negative influences on breeding success but it is recognized that for such a long-lived bird adult survival is also likely to be an important limiting factor on the population size.     

Stable isotopes in southern rockhopper penguins: foraging areas and sexual differences in the non-breeding period

Southern rockhopper penguins (Eudyptes chrysocome chrysocome) have experienced severe population declines across their distribution area, potentially in response to bottom-up effects following elevated sea surface temperatures, changes in the food web and prey availability. We conducted stable isotope analysis to compare trophic levels and distribution patterns in the non-breeding period over three consecutive years, and between males and females, using egg membranes, blood cells and feathers of parent birds. Tissues representing the non-breeding season had lower ??¹³C values than prey sampled around the Falklands and red blood cells from breeding rockhopper penguins. In contrast, ??¹⁵N values were higher in red blood cells from the end of winter compared to those from the breeding season and compared to feathers. This indicated that rockhopper penguins left the Falkland Island area in the non-breeding season and foraged either around Burdwood Bank further south, or over the Patagonian Shelf. In winter, only males took more prey of higher trophic level than females. Inter-annual differences in isotopic values partly correlated with sea surface temperatures. However, as prey isotope samples were collected only in 1?year, inter-annual differences in penguin isotopic values may result from different foraging sites, different prey choice or different isotopic baseline values. Our study highlights the potential for stable isotope analyses to detect seasonal and gender-specific differences in foraging areas and trophic levels, while stressing the need for more sampling of isotopic baseline data.     

To breed or not to breed: causes and implications of non-breeding habit in the willow tit Parus montanus

Causes and consequences of non-breeding in willow tits were studied in northern Finland during 1986–1992. The breeding status was sex and age biased; males and yearling birds were in excess among the non-reproducers. Due to sex bias in the population it appeared detrimental for males to lose a mate, especially shortly before breeding. Lack of a mate was a important factor for males not reproducing (37% of non-breeding males) than for females (14%). Most of the non-breeding birds maintained a pair bond which only rarely broke up for the next breeding season (divorce rate 5.5%). This implies that parental incompatibility is not a possible explanation for pairs not reproducing. Males that did not breed tended to survive better than reproducing ones, whereas such a relationship was not found for females. It is possible that this sex-related difference in survival cost is attributable to quality differences among non-breeding individuals. It was especially low-quality yearling females, with low survival prospects, that were responsible for the discrepancy. The proportion of non-breeding females in the population correlated highly with clutch size and subsequent juvenile survival. It is therefore suggested that for most of these females non-breeding is a phenotypic response to low offspring value in the prevailing circumstances (inter-generational tradeoff). However, it is uncertain whether willow tits in a northern population can use breeding density as an indicator of changing survival prospects of their descendants, as suggested by Ekman and Askenmo (1986) for southern Sweden.     

A SOCIO-ECOLOGY OF MAGPIES PICA PICA

The behaviour and ecology of unmarked Magpies Pica pica living in the Cotswolds were investigated over 18 months. The spacing of nests was significantly more regular than random and breeding pairs defended territories throughout the year. In winter pairs occasionally left territories to feed with non-breeding birds which flocked throughout the year.
Magpies in flocks had a higher averiage feeding rate than birds alone or in pairs. Aggression rates in flocks increased as birds fed closer together and as food patches became richer.
Agonistic interactions between Crows Corvus corone and Magpies were common; Crows frequently dominated Magpies in disputes over food, and Crows also ate Magpie eggs and young. Single Magpies were most often chased by Crows while Magpies in flocks were able to feed longer in the presence of Crows.
Differences in fledgling success among breeding pairs were related to the location of nests; Magpie pairs breeding near Crow nests suffered higher rates of agonistic encounters with Crows and also produced fewer fledglings than did Magpies breeding at greater distances from Crow nests. Magpie nests were located nearer human habitations than were Crow nests.     

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.     

Weak migratory connectivity,loop migration and multiple non-breeding site use in British breeding Whinchats Saxicola rubetra

Determining the links between breeding populations and the pressures, threats and conditions they experience presents a challenge for the conservation of migratory birds which can use multiple sites separated by hundreds to thousands of kilometres. Furthermore, migratory connectivity – the connections made by migrating individuals between networks of breeding and non-breeding sites – has important implications for population dynamics. The Whinchat Saxicola rubetra is declining across its range, and tracking data from a single African non-breeding site implies high migratory spread. We used geolocators to describe the migration routes and non-breeding areas of 20 Whinchats from three British breeding populations. As expected, migratory spread was high, with birds from the three populations overlapping across a wide area of West Africa. On average, in non-breeding areas, British breeding Whinchats were located 652 km apart from one another, with some likely to share non-breeding areas with individuals from breeding populations as far east as Russia. Four males made a direct non-breeding season movement to a second, more westerly, non-breeding location in January. Autumn migration was through Iberia and around the western edge of the Sahara Desert, whereas spring migration was more direct, indicating an anticlockwise loop migration. Weak migratory connectivity implies that Whinchat populations are somewhat buffered against local changes in non-breeding conditions. If non-breeding season processes have played a role in the species’ decline, then large-scale drivers are likely to be the cause, although processes operating on migration, or interactions between breeding and non-breeding processes, cannot be ruled out.     

Age composition of winter irruptive Snowy Owls in North America

Patterns of winter irruptions in several owl species apparently follow the ‘lack of food’ hypothesis, which predicts that individuals leave their breeding grounds in search of food when prey populations do not allow breeding and are too small to ensure survival. Recent analyses, however, suggest an alternative mechanism dubbed the ‘breeding success’ hypothesis, which predicts that winter irruptions might instead be the result of a very successful breeding season, with a large pool of young birds subsequently migrating south from the breeding grounds. Here we assessed age‐class (juvenile vs. non‐juvenile) composition of winter irruptive Snowy Owls Bubo scandiacus over a 25‐year period (winter 1991–1992 to 2015–2016) between regular (North American Prairies and Great Plains) and irregular wintering areas (northeastern North America) using live‐trapped individuals and high‐resolution images of individual owls. Our results show that the proportion of juveniles (birds less than 1 year of age) varies considerably annually but is positively correlated with irruption intensity in both regions. In irregular wintering areas, it can constitute the majority (up to more than 90%) of winter irruptive Snowy Owls over a large geographical area. These results are consistent with the idea that large winter irruptions at temperate latitudes are not the result of adults massively leaving the Arctic in search of food after a breeding failure but are more likely to be a consequence of good reproductive conditions in the Arctic that create a large pool of winter migrants.     

Light pollution enhances ground-level exposure to airborne toxic chemicals for nocturnally migrating passerines

Anthropogenic activities generate different forms of environmental pollution, including artificial light at night (ALAN) and airborne toxic chemicals (ATCs). Nocturnally migrating birds are attracted to ALAN during migration and if ALAN occurs in unison with ATC, the chances of ground-level ATC contamination occurring at stopover sites could increase. Here, we document the relationship between ALAN and ATC within the contiguous United States based on 479 toxic chemicals from 15,743 releasing facilities. Using weekly diurnal estimates of relative abundance for 165 nocturnally migrating passerine (NMP) bird species, we assess how the species richness and relative abundance of NMP species are correlated with ALAN and ATC across the annual cycle. The concentration of ATC increased with increasing ALAN levels, except at the highest ALAN levels. The species richness of NMP species was positively correlated with ATC during the non-breeding season and migration, and negatively correlated during the breeding season. The relative abundance of NMP species was negatively correlated with ATC during the breeding and non-breeding seasons and the correlation did not differ from zero during migration. Through the disorienting influence of ALAN, our findings suggest large numbers of NMP species are being exposed to higher ATC concentrations at stopover sites. Outside of migration, large numbers of NMP species that winter along the US Gulf Coast are being exposed for an extended period of time to higher ATC concentrations. Initiatives designed to decrease ALAN during migration have the potential to reduce the acute and chronic effects of ATC contamination, lower the maternal transfer of toxic chemicals to eggs, and decrease the biologically mediated transport of toxic chemicals across regions. However, these initiatives will not benefit species that experience prolonged ATC exposure during the non-breeding season along the US Gulf Coast, a region that could be a significant source of ATC contamination for North American birds.     

The breeding biology of the Common Crossbill Loxia curvirostra in the Central Pyrenees

The breeding biology of the Common Crossbill Loxia curvirostra was studied over ten consecutive years in forests of Mountain Pine Pinus uncinata in the Pyrenees, France. The breeding season lasts from summer to the next spring following the maturation and the opening of the pine cones. Pairs with dependent young were most common in November and March–May. The greatest number of clutches was observed in December and January (53%, n = 30). Average clutch size was 3.43 eggs (sd = ±0.57; n = 30), the number of fledged young was 1.32 per completed clutch (sd = ±1.7; n = 25) and the proportion of breeding attempts that were successful was 27.8% in the winter/spring period (n = 36). The number of successful pairs was found to be positively correlated to the number of cones, and in the winter/spring period negatively correlated to the mean depth of snow. Breeding only failed completely during the year in which the density of birds was highest. In years with a good cone crop, breeding that starts early and continues over a long period appears to be an adaptation which increases productivity in this sedentary population dependent on fluctuating food resources. An irruption by birds from northern Europe in 1990 did not affect the numbers or breeding success of the Pyrenean crossbills.