Hani Amir Aouissi, Mostefa Ababsa, Aissam Gaagai, Zihad Bouslama, Yassine Farhi, Haroun Chenchouni. 2021: Does melanin-based plumage coloration reflect health status of free-living birds in urban environments?. Avian Research, 12(1): 45. DOI: 10.1186/s40657-021-00280-7
Citation: Hani Amir Aouissi, Mostefa Ababsa, Aissam Gaagai, Zihad Bouslama, Yassine Farhi, Haroun Chenchouni. 2021: Does melanin-based plumage coloration reflect health status of free-living birds in urban environments?. Avian Research, 12(1): 45. DOI: 10.1186/s40657-021-00280-7

Does melanin-based plumage coloration reflect health status of free-living birds in urban environments?

Funds: 

the DGRSDT and MESRS Ministry of Higher Education and Scientific Research of Algeria

More Information
  • Corresponding author:

    Haroun Chenchouni, chenchouni@gmail.com

  • Received Date: 18 Oct 2020
  • Accepted Date: 01 Sep 2021
  • Available Online: 24 Apr 2022
  • Publish Date: 13 Sep 2021
  • Background 

    Ecological functions and processes in urban ecosystems are governed by various human activities. City-adapted and city-exploiting animal species are expected to present certain specific behavioral and physiological traits in comparison to city-avoiders or conspecific individual frequenting less urbanized or rural environments. A trait of high importance, the plumage color polymorphism has been selected as the main study model and was correlated with different morphological and physiological parameters to highlight its importance in determining the possible health status of urban Feral Pigeons (Columba livia) in North African urban habitats.

    Methods 

    Different body morphometrics, hematological and hemoparasitic parameters were quantified on free-living Feral Pigeons in urban environments of northern Algeria. Moreover, plumage melanin-based coloration (MBC) was measured and the data collected at the individual scale was correlated with the previous parameters using linear and non-linear modeling approaches.

    Results 

    Plumage MBC scores of the sampled Feral Pigeons ranged between 0.3% and 74.8%. Among the 12 morphological traits measured, body weight, tail length and total length were deemed to be positively correlated with MBC. Darker morphs appeared to have more hemoparasites compared to lighter pigeons. Quite the same observation goes with the immunity but with non-linear trends. The number of monocytes and granulocytes increased with the increase in MBC levels in lighter morphs, while pigeons with high MBC scores exhibited negative relationships between MBC levels and the number of white blood cells.

    Conclusions 

    Despite the existence of a number of studies demonstrating phenotypic directional selection, further studies are undoubtedly necessary to understand in detail the underlying mechanisms in species life-history strategies between differently colored individuals. Findings of this correlative study open exciting perspectives revealing that MBC can be considered a good indicator of and health status and adaptation strategies to changes in urban environments.

  • The brood parasitic Common Cuckoos (hereafter "Cuckoo"; Cuculus canorus) lay eggs into nests of other bird species, and the Cuckoo chick evicts all nest contents, eggs or nestlings, after hatching, typically causing the failure of all host offspring. This represents a high cost of parasitism for the hosts (Davies, 2000; Kilner, 2006). However, future prospects of the cuckoo eggs depend on host egg recognition and their decision on egg discrimination. Hosts may possess the ability to recognize and reject the parasite egg (Davies and Brooke, 1989; Moksnes et al., 1991; Hauber and Sherman, 2001), so natural selection favors the development of mimetic foreign eggs (Davies, 2000). Mimicry of the parasites' eggs in relation to host eggs may reach high levels in some populations (Moksnes and Røskaft, 1995; Igic et al., 2012).

    Acrocephalus warblers are favored hosts of the cuckoo in the Palearctic (Johnsgard, 1997; Payne, 2005; Leisler and Schulze-Hagen, 2011). In East-Central Europe the Great Reed Warbler (Acrocephalus arundinaceus) is a frequently used host (e.g. Moksnes et al., 1993; Moskát and Honza, 2000, 2002; Trnka and Prokop, 2011). In Hungary, parasitism rate reaches an unusually high level (41–68%; Moskát et al., 2008b), instead of the typical 1–10% (Davies, 2000). In this area mimicry of the Cuckoo eggs in relation to host eggs often shows a high degree (Southern, 1954; Moskát and Honza, 2002; Cherry et al., 2007a). As the size of a Cuckoo egg is similar to the size of a Great Reed Warbler egg (e.g., Hargitai et al., 2010), the recognition of a Cuckoo egg sometimes needs special caution for the human observer (but the result is almost 100%; C. Moskát, unpubl.). However, the recognition of the Cuckoo eggs seems to be more difficult for Great Reed Warblers than for human observers: they accepted 66% of the Cuckoo eggs, and rejected the rest by egg ejection (12%), nest desertion (20%) and egg burial (2%) (Moskát and Honza, 2002). The typically good, sometimes perfect mimicry of the Cuckoo eggs are regarded as the result of the coevolutionary process between hosts and brood parasites (Brooke and Davies, 1988; see for reviews in Davies, 2000, 2011; Krüger, 2007). Cuckoo hosts discriminate against poorly matching parasitic eggs (Davies and Brooke, 1988; Moskát and Honza, 2002; Cherry et al., 2007a; Yang et al., 2010; Vikan et al., 2011). Consequently, parasite egg mimicry is expected to be increasing over time (Takasu, 1998).

    In Japan, Common Cuckoos also parasitize a closelyrelated Acrocephalus species, the Oriental Reed Warbler (Acrocephalus orientalis), which previously was not separated from the Great Reed Warbler, but regarded as one of its subspecies (A. arundinaceus orientalis). Oriental Reed Warblers are also parasitized in a relatively high frequency (8–22%; Lotem et al., 1995), but lower than Great Reed Warblers in Hungary (see above). The Japanese population of Oriental Reed Warblers at Nagano City also showed antiparasite defenses against Cuckoo eggs, where different studies revealed 62% (Lotem et al., 1995) or 45% rejection rates towards Cuckoo eggs (Nakamura et al., 1998).

    Rejection of parasite eggs by hosts is an important indicator of host adaptations to cuckoo parasitism (Davies and Brooke, 1989; Moksnes et al., 1991; Lovászi and Moskát, 2004; Stokke et al., 2005), as well as to other brood parasites (e.g., Davies 2000; Begum et al. 2011; de la Colina et al., 2012). Most of previous studies used model Cuckoo eggs in experimental parasitism, for studying egg rejection behavior of hosts (reviews in Davies, 2000; Kilner, 2006; Krüger, 2007). Much fewer studies have revealed egg discrimination of hosts against naturally parasitized Cuckoo eggs, typically in Acrocephalus warblers (e.g., Davies and Brooke, 1988; Lotem et al., 1992; Moksnes et al., 1993; Moskát and Honza, 2002; Cherry et al., 2007a; Honza et al., 2011). As vision of many bird species covers a wider range of reflectance spectra (300–700 nm) than that of humans (Bennett and Cuthill, 1994), UV-VIS spectrophotometers have proved to be most useful to evaluate egg mimicry (Cherry et al., 2007a).

    As both the Japanese and the Hungarian populations of the above-mentioned Acrocephalus hosts show moderately developed antiparasite defenses, it may be a reflection of that both the host and brood parasite populations have been in contact with each other. Although the two populations of the two studied warblers may be different in their evolutionary history, including their coevolution with the Cuckoo, this case offers a unique situation for the comparison of egg mimicry and antiparasite defense in two distant areas. Hostbrood parasite coevolution might take several alternative directions regarding egg appearances in time and space (Dawkins and Krebs, 1979; Rothstein, 1990), while still maintaining the adaptive value of egg coloration (Underwood and Sealy, 2002; Kilner, 2006). Although brood parasitism is a dominant selective agent forcing the development of Cuckoo egg characteristics (Stokke et al., 2002; Kilner, 2006), we have no previous knowledge if hosts and brood parasites follow the same scenario in their coevolution at two distant sites. However, modeling coevolution has revealed several alternative potential pathways for Cuckoos and their hosts (Takasu, 1998, 2003; Barabás et al., 2004; Røskaft et al., 2006; Takasu and Moskát, 2011).

    In this paper, we compared main characteristics of Cuckoo parasitism on two relatively large-sized Acrocephalus species in Japan and Hungary. We analyzed spectrophotometric data by visual models taking into account the sensitivity to different wavelengths of the four cone types in the avian retina (Endler and Milke, 2005). This method let us incorporate the effects of avian perceptual properties as it has recently been applied and recommended for the comparison of color attributes of Cuckoo and host eggs (e.g., Cassey et al., 2008; Avilés, 2008; Langmore et al., 2009; Antonov et al., 2010; Stoddard and Stevens, 2010; Vikan et al., 2011). Following the idea of the arms race hypothesis (Dawkins and Krebs, 1979; Davies, 2000; Krüger, 2007) applied for the coevolution between the Cuckoo and its hosts, we predicted that Cuckoos developed adaptations to host rejection by developing mimetic eggs in both areas. We also examined host responses to Cuckoo parasitism in the two distant areas, and predicted higher similarities between accepted eggs and lower similarities between eggs which were rejected. Finally, we predicted that the Cuckoo egg mimicry and host egg rejection behavior are similar in the two areas, indicating a similar level of coevolutionary adaptations.

    The study was carried out at two sites: (1) Nobeyama highlands (35°57'N, 138°28'E), ca. 120 km south of Nagano city, central Japan. In this area Oriental Reed Warblers breed in small patches of reeds (Phragmites australis and Miscanthus sacchariflorus) along small (1–2 m wide) streams, and reed patches are surrounded by wooded vegetation composed primarily of maple trees (Acer ginnala) and willow bushes (Salix integra). The study was conducted during May–July 2004. (For more details of the habitat, see Muñoz et al., 2007). (2) In the surroundings of Apaj (47°07'N, 19°06'E), ca. 50 km south of Budapest in the Hungarian Great Plains, central Hungary. Here Great Reed Warblers breed in 2–4 m wide stripes of reed (Phragmites australis) growing along both sides of small (5–10 m wide) channels. Lines of trees (hybrid poplars, Populus alba, Salix cinerea, Elaeagnus angustifolia) and bushes typically follow the channels, although treeless sections also occur. (For more details of the habitat, see Moskát and Honza, 2000, 2002). Only those nests containing one Cuckoo egg and at least one host egg, and if the hosts' response to parasitism was known, were used for analyses.

    We systematically searched for nests in parts of the study area ca. twice per week. Nests in the egg laying stage were controlled daily. Nests parasitized by a Cuckoo were controlled for six consecutive days to observe host reactions, and used to categorize host responses to parasitism. This 6-day (or 5-day) long period for monitoring hosts' reactions is typically used in studies of natural Cuckoo parasitism (e.g., Lotem et al., 1995; Moskát and Honza, 2002) and experiments with model Cuckoo eggs (e.g., Moksnes et al., 1991; Bártol et al., 2002). Host responses were categorized as acceptance or rejection of the Cuckoo egg. The term rejections included egg ejections and nest desertions (see more details on the method of nest monitoring in Moskát and Honza, 2002).

    Eggs were photographed using digital cameras (Olympus E-20 and Nikon CoolPix 995) on Kodak grey card with Kodak control color patches. We measured reflectance spectra (300–700 nm) from the eggshells by spectrophotometers type Ocean Optics USB 2000, which interval covers the range of the vision of small passerines (e.g., Bennett and Cuthill, 1994; Endler and Milke, 2005). All eggs were measured in a clutch, although not all clutches were measured by spectrophotometer, so sample sizes slightly differ for host responses and egg characteristics. We measured reflectances at eight points on the eggshell, i.e., two measurements at four zones of the eggs, dividing the eggshell surface into four equally long parts along the long axis (see for more details on measuring reflectances from eggs in Takasu et al., 2009). A conceptually similar method, when the eggshell surface is divided into segments along the long axis, was developed by Cherry and Bennett (2001).

    For the evaluation of chromatic difference (∆TC) among Cuckoo and host eggs we applied the perceptual models developed for avian vision (Kelber et al., 2003; Endler and Milke, 2005). These models provide a useful way for the quantification of color difference between eggs as birds can see, with respects to the spectral sensitivities of the avian single cone photoreceptors in the retina (Vorobyev and Osorio, 1998). In birds the four single photoreceptors are sensitive to certain parts of the whole spectra within 300 and 700 nm, called ultraviolet, short-wavelength, medium-wavelength and long-wavelength (Hart et al., 2000). In comparison of color differences between Common Cuckoo and host eggs these models have already been useful (e.g., Avilés, 2008; Cassey et al., 2008; Antonov et al., 2010; Vikan et al., 2011), and also for other brood parasite-host relationships (Langmore et al., 2009; Spottiswoode and Stevens, 2010). We used the "woodland canopy-filtered green light" (also called "green leaves"; Endler, 1993) and "open nest" (Avilés, 2008) ambient light conditions for ambient irradiance in the perceptual models, as Acrocephalus warblers typically breed in open nests in the reeds, in the shade of long reed leaves. We also calculated achromatic contrast (∆TQ) expressing brightness differences between Cuckoo and host eggs. Chromatic and achromatic differences are expressed in just noticeable difference thresholds (JNDs), where a value above the JND = 1 threshold suggests that the cuckoo egg can be discriminated from the host eggs, but a value below this threshold suggests that the parasitic egg is undistinguishable (Osorio and Vorobyev, 1996, see for more details in Avilés, 2008 and Igic et al., 2012). For visual modeling we used Avicol version 4 (Gomez, 2010).

    In the present study we focused on the importance of chromatic and achromatic components of eggshell characteristics in coevolution between brood parasites and their hosts, but spottiness may also have some relevance (Polaciková and Grim, 2010). However, the fiber optic probe of our spectrophotometer only allows samples from larger spots, only > 2 mm in diameter, which is not suitable for speckles or lines. Experimental studies on the Hungarian Great Reed Warbler population has shown that small spots may be important in egg recognition (Moskát et al., 2008a), but the role of larger spots is not so clear (Moskát et al., 2008c).

    We used generalized linear models to test the dependent variable (acceptance versus rejection), involving intercept, country as independent fixed factor, chromatic difference (∆TC), and achromatic difference (∆TQ) as covariates. We also involved the interaction terms chromatic difference×country and achromatic difference ×country. Data were analyzed with SPSS version 17.0 (SPSS, Inc.). We applied the Levene's test for testing homogeneity of variances prior to parametric tests.

    Some of the Cuckoo eggs found in Hungary showed a good mimicry to host eggs, while in general mimicry was lower in Japan (Fig. 1). Although the main characteristics of host eggs were similar in Japan and Hungary, Cuckoos in Japan often showed red markings, sometimes with the special line pattern (Fig. 1). Visual modeling on spectrophotometer measurements revealed that chromatic difference between Cuckoo and host eggs was lower in Hungary than in Japan, whereas the achromatic difference showed the opposite trend (Fig. 2; open nest ambient light conditions, Mann-Whitney U-tests were significant for both the chromatic and achromatic cases: U = 100.00, p = 0.049). The values of chromatic difference did not differ significantly from the just noticeable difference threshold (JND = 1) (ones-sample t-test, t17 = 0.910, p = 0.375) in Hungary, which means that Cuckoo eggs are more difficult to recognize in Hungary than in Japan, where chromatic difference exceeded the threshold significantly (t17 = 2.948, p = 0.009). However, the achromatic difference between parasite and host eggs did not differ from the threshold in Japan (two-sample t-test, t17 = 0.867, p = 0.398), but it was significantly different in Hungary (t17 = 3.244, p = 0.005). We found similar results when the green ambient light conditions was used for calculation (Hungary: chromatic contrast: t17 = 0.505, p = 0.620, achromatic contrast: t17 = 3.246, p = 0.005; Japan: chromatic contrast: t17 = 2.461, p = 0.025, achromatic contrast: t17 = 0.887, p = 0.388).

    Figure  1.  Types of egg morphs of Common Cuckoos (Cuculus canorus) and their two closely-related Acrocephalus hosts from Hungary (host: Great Reed Warbler, A. arundinaceus) and Japan (host: Oriental Reed Warbler, A. orientalis)
    Figure  2.  Mean perceived differences (±S.E.) for the chromatic and achromatic components of color matching between the eggs of Common Cuckoos and their two closely-related Acrocephalus hosts, i.e., the Oriental Reed Warbler in Japan and Great Reed Warbler in Hungary. Asterisks indicate significant difference from the just noticeable difference threshold, JND = 1, at the p ≤ 0.05 level, obtained by onesample t-test.

    We observed host reactions toward Cuckoo eggs in 37 nests. Rejection rates against single Cuckoo eggs were similar at the two sites (7/19 in Hungary and 7/18 in Japan; Fig. 3; χ12 = 0.02, p = 0.898). Parasitism rate was higher in Hungary than in Japan (28/46 nests, i.e., 61% parasitism rate in Hungary and 22/57 nests, i.e., 39% in Japan in 2004), however, the difference was not statistically significant (χ12 = 1.73; p = 0.188).

    Figure  3.  Parasitism rates and rejection rates of Common Cuckoo eggs in two closely-related Acrocephalus species at distant areas, i.e., the Oriental Reed Warbler in Japan and Great Reed Warbler in Hungary

    Generalized linear models on egg characteristics of the two Acrocephalus species revealed no direct effect of chromatic and achromatic difference between host and parasite eggs on the rejection of Cuckoo eggs. However, we revealed significant effects of country and the term of interaction between country and achromatic distance (∆TQ) in the generalized linear model, while achromatic distance without the interaction term proved not to be significant (country: χ2 = 3.90, p = 0.048; ∆TC: χ2 = 0.24, p = 0.628; ∆TQ: χ2 = 3.31, p = 0.069; country×∆TC: χ2 = 0.41, p = 0.524; country×∆TQ: χ2 = 5.90, p = 0.015; intercept: χ2 = 0.04, p = 0.853).

    Regarding eggshell colors, our analyses revealed a higher similarity of Cuckoo eggs with respect to host eggs in Hungary than in Japan. It is an important indicator of coevolutionary adaptations, as mimicry of Cuckoo eggs is expected to increase over time during Cuckoo parasitism (see review by Davies, 2000). Although exact time when Cuckoo parasitism started is not known, neither for the Great Reed Warbler in Hungary, nor the Oriental Reed Warbler in Japan, circumstantial evidence suggests that the history of these coevolutionary interactions reflects a longer history in the Western Palearctic than in the Eastern Palearctic. Recent Cuckoo parasitism is estimated for more than 110 years in Hungary, since parasitized Great Reed Warbler clutches with Cuckoo eggs were already collected ca. 110 years ago and stored in museums (C. Moskát unpubl.). Cuckoo parasitism started ca. 50 years ago in the Nobeyama district, but probably it started earlier in other parts of Japan (Nakamura, 1990). In Hungary, Cuckoos have developed almost perfect mimicry regarding background and spot colors and spottiness of eggs, but not in egg shape (Bán et al., 2011). On the one hand, high interclutch variation of hosts makes it more difficult for the Cuckoo to match the host eggs even when Cuckoo eggs show perfect mimesis to one type of Great Reed Warbler eggs (Moskát and Honza, 2002). On the other hand Cuckoos selecting actively for proper nests may increase their success of matching (Cherry et al., 2007b; see also Avilés et al., 2006).

    Cuckoo eggs in the Hungarian study area are found to be polymorphic (Moskát and Honza, 2002), therefore, even cuckoo eggs showing poor mimesis to host eggs can be found in the area. For example, one poorly mimetic egg type, the so-called Garden Warbler (Sylvia borin)-type Cuckoo egg was also found in the study area, which seems to be a generalist Cuckoo egg-type in central Europe (Lovászi and Moskát, 2004). This egg type has also been reported from the Czech Republic (Edvardsen et al., 2001; Honza et al., 2001). Interestingly, the Garden Warbler-type Cuckoo egg morph found in Hungary had a high similarity with Garden Warbler eggs from Germany, but this egg morph is different from Garden Warbler eggs in Hungary (C. Moskát, unpubl.). In the 1920s a system of flood relief and irrigation channels was established in Hungary, offering a preferable habitat with narrow reed beds along both sides of the channels. This habitat offered the open water surface-reed edge for birds, which is favored by Great Reed Warblers (Báldi and Kisbenedek, 2000). Although in the Hungarian Great Plains wetland habitats dominated originally, they were lost gradually. However, extensive work to control rivers' flood during the second half of the 19th century made numerous dead branches, especially suitable habitats for the Great Reed Warbler (Molnár, 1944). We therefore suppose that Cuckoos started to parasitize this warbler extensively in the dead branches, and, later, in the channels depending on the availability of trees used for vantage points by nest searching Cuckoos (Moskát and Honza, 2000). The possible origin of recent Cuckoo parasitism on the Great Reed Warbler was the parasitism on several Acrocephalus species, including the Great Reed Warbler, Reed Warbler (A. scirpaceus), Sedge Warbler (A. schoenobaenus) and Marsh Warbler (A. palustris), because parasitized clutches of these species can be found from the first half of the 20th century in Hungarian bird egg collections (C. Moskát, unpubl.). However, recent parasitism on these three smaller Acrocephalus species seems to be scarce (C. Moskát, unpubl.).

    In Japan the different Cuckoo gentes are less separated than in Europe (Higuchi, 1998; Nakamura et al., 1998). The Bunting-type Cuckoo eggs seem to be the ancient form, and probably Cuckoos of several host species radiated from this gens (c.f. Nakamura et al., 1998; Takasu et al., 2009). Although the Siberian Meadow Bunting (Emberiza cioides) used to be the most Common Cuckoo host in the first half of the 20th century (Nakamura et al., 1998), it is presently almost abandoned by Cuckoos. This host species developed high level egg discrimination ability, and, consequently, Cuckoos expanded the number of their hosts. Many Cuckoo eggs exhibit small lines as pigments on the eggshell (Nakamura et al., 1998; Takasu et al., 2009), which is not typical for European Cuckoos. In our study area at Nobeyama, in central Japan, four host species are frequently parasitized by Cuckoos: Black-faced Buntings (E. spodocephala), Bull-headed Shrikes (Lanius bucephalus), Azure-winged Magpies (Cyanopica cyana) and Oriental Reed Warblers. Cuckoo eggs parasitizing these four host species seem to be similar, but some early separation was revealed by a recent spectrophotometer study (Takasu et al., 2009). The bunting-type Cuckoo egg morph matches well the eggs of Bull-headed Shrikes, but it is non-mimetic for the Azure-winged Magpie and Oriental Reed Warbler. So the Japan Cuckoo-host relationship is a sympatric multihost system, as Cuckoos parasitize several host species at the same location. Although these hosts prefer different habitats, the imperfect isolation of these host populations from each other slows down adaptational mechanisms (sensu Møller et al., 2011). The presence of lines as egg markings on Cuckoo eggs in Japan is unique when compared either to Cuckoo eggs in Hungary, or any of the studied Acrocephalus hosts (Fig. 1). This special marking on Cuckoo eggs may also reduce mimicry between Oriental Reed Warbler and Cuckoo eggs. Contrary, in the Hungarian Great Plane Cuckoos parasitize only one dominant host species, the Great Reed Warbler. There is another frequently used host species in Hungary, the Robin (Erithacus rubecula), which shows a strong separation from Great Reed Warblers by habitat, as Robins occur in the woodlands of hilly areas (Fuisz and de Kort, 2007).

    Rejection rates in the two Acrocephalus Warbler populations proved to be highly similar, despite the differences in Cuckoo egg mimicry. This finding suggests that coevolutionary mechanisms, i.e., hosts' antiparasite defences, and Cuckoos' counter-adaptations to hosts by mimetic eggs may have different speed. Thus coevolutionary interactions are probably less synchronized than predicted by the arms race model (Dawkins and Krebs 1979; Davies 2000; Krüger 2007). This might be due to hosts' immigration from nearby, highly productive, probably unparasitized or less parasitized source populations in a metapopulation structure (Barabás et al., 2004). Immigration of hosts with less developed antiparasite defense might result in reduced egg discrimination ability in the Hungarian study area. This process might explain the similar level of egg rejection in Japan and Hungary, even though, the Hungarian Cuckoo-Great Reed Warbler system is more developed, as indicated by the higher level of mimesis of Cuckoo eggs here.

    A previous study on the Oriental Reed Warbler in Nagano district, Japan (ca. 120 km away from our study www.chinesebirds.net site in Nobeyama district) revealed an even higher rejection rate than our study revealed (62% vs 39%) towards natural Cuckoo eggs between 1989 and 1991 (Lotem et al., 1995). The population in Nagano district started to be parasitized only 30 years ago, so it is likely that some parts of egg discrimination is the result of a former interaction with the Cuckoo, or due to gene flow from other areas (Lotem et al., 1995).

    Our results revealed similar efficiency in egg rejection behavior of the two Acrocephalus studied hosts, which can be regarded as one of the most important indicators of hosts' evolutionary adaptation to brood parasitism. On the other hand, we also revealed better mimicry of Cuckoo eggs to host eggs in Hungary than in Japan. The origin of Cuckoo parasitism on the Great Reed Warbler in Hungary differs from that of the Oriental Reed Warbler in Japan. While Cuckoos might have radiated from the Bunting Cuckoo-gens in Japan, in Hungary the Great Reed Warbler-Cuckoo gens probably originated from the Acrocephalus group. It is a surprising result that Japanese Cuckoos show low level mimicry to Oriental Reed Warbler eggs, although this warbler species possess a moderate egg rejection ability. Theoretically, in such type of systems better parasite egg mimicry is expected, as simulation models have revealed (Takasu, 2003). There are two possible explanations for this interesting result. At one hand there is a multihost system in central Japan, which might slow down separation of Cuckoos into distinct gentes (c.f. Higuchi, 1998; Nakamura et al., 1998). Takasu (2003) showed by simulation models, if the host population is polymorphic regarding egg morphs, this might prevent Cuckoos to develop a better mimicry.

    Host aggression against the Cuckoo may also be evolved during sympatry with the brood parasite, and typically coevolves with egg rejection ability (Røskaft et al., 2002). As hosts breed in similar habitats in our two study sites, we think that host defense plays the most important role in Cuckoo-host coevolutions in these cases. In Hungary Great Reed Warblers show high aggression against the Cuckoo (85% attack, n = 40; Bártol et al., 2002), but Oriental Reed Warblers attacked Cuckoos at a lower frequency (38%; Andou et al., 2005). However, sample size in the Japanese study was low (n = 8).

    We conclude that despite of the dissimilar features of Cuckoo-Warbler coevolution in Japan and Hungary, including possible different origins of parasitism and levels of parasitic pressure, Cuckoos showed adaptations to host eggs at varying degrees of egg mimicry, and hosts developed egg discrimination behavior against Cuckoo eggs. Hosts' egg discrimination proved to be very similar in the two host-brood parasite systems, although the pattern of egg mimicry is clearly different. Our results suggest that Cuckoos and Warblers followed different pathways of coevolution in the two distant areas, and they seem to be at different stages in the arms race.

    The authors are thankful to Tibor Kisbenedek, László Bagó, István Bártol and Kinga Iglói for their assistance in the field work. For discussions we thank Maria Altamirano, Michael I. Cherry, Marcel Honza, Rita Hargitai, Branislav Igic and many other colleagues. We thank two anonymous reviewers and the guest editors for helpful comments on our manuscript. The study was supported by the bilateral project of the Japan Society for the Promotion of Science (JSPS) and the Hungarian Academy of Sciences to F.T. and C.M. 2003-2005, and by the Hungarian Scientific Research Fund (OTKA; grant No. T35015, 48397 and 83217) to C.M. The Duna-Ipoly and Kiskunság National Parks provided permissions for research.

  • Almasi B, Jenni L, Jenni-Eiermann S, Roulin A. Regulation of stress response is heritable and functionally linked to melanin-based coloration. J Evol Biol. 2010;23: 987–96.
    Aouissi HA, Belabed AI, Bouslama Z. Doves' mapping and inventory into the urban sites of Annaba (Northeastern of Algeria). Adv Environ Biol. 2015;12: 328–38.
    Aouissi HA, Gasparini J, Belabed AI, Bouslama Z. Impact of greenspaces in city on avian species richness and abundance in Northern Africa. CR Biol. 2017;340: 394–400.
    Aouissi HA, Petrişor AI, Ababsa M, Boştenaru-Dan M, Tourki M, Bouslama Z. Influence of land use on avian diversity in North African urban environments. Land. 2021;10: 434.
    Aouissi HA. Écologie des espèces aviaires dans le tissu urbain de la ville de Annaba. Doctoral Thesis. Annaba: University of Annaba; 2016.
    Barber I, Dingemanse NJ. Parasitism and the evolutionary ecology of animal personality. Philos Trans R Soc B. 2010;365: 4077–88.
    Barcia JJ. The Giemsa stain: its history and applications. Int J Surg Pathol. 2007;15: 292–6.
    Belabed AI, Aouissi HA, Zediri H, Djemadi I, Driss K, Houhamdi M, et al. The effect of urbanization on the phenotype of the Collared Dove (Streptopelia decaocto) in northeastern Algeria. Bull Inst Sci Rabat. 2013;35: 155–64.
    Belabed BE, Meddour A, Samraoui B, Chenchouni H. Modeling seasonal and spatial contamination of surface waters and upper sediments with trace metal elements across industrialized urban areas of the Seybouse watershed in North Africa. Environ Monit Assess. 2017;189: 265.
    Bendjoudi D, Chenchouni H, Doumandji S, Voisin JF. Bird species diversity of the Mitidja Plain (Northern Algeria) with emphasis on the dynamics of invasive and expanding species. Acrocephalus. 2013;34: 13–26.
    Bendjoudi D, Voisin JF, Doumandji S, Merabet A, Benyounes N, Chenchouni H. Rapid increase in numbers and change of land-use in two expanding Columbidae species (Columba palumbus and Streptopelia decaocto) in Algeria. Avian Res. 2015;6: 18.
    Berry JL. Urbanization. The earth as transformed by human action. In: Turner II BL, Clark WC, Kates RW, Richards JF, Mathews JT, Meyer WB, editors. The earth as transformed by human action: global and regional changes in the biosphere over the past 300 years. Cambridge: Cambridge University Press, UK; 1990. p. 103–19.
    Blair R. The effects of urban sprawl on birds at multiple levels of biological organization. Ecol Soc. 2004;9: 2.
    Blanchet S, Méjean L, Bourque JF, Lek S, Thomas F, Marcogliese DJ, et al. Why do parasitized hosts look different? Resolving the "chicken-egg" dilemma. Oecologia. 2009;160: 37.
    Borras A, Pascual J, Senar JC. What do different bill measures measure and what is the best method to use in granivorous birds? J Field Ornithol. 2000;71: 606–11.
    Bradley CA, Altizer S. Urbanization and the ecology of wildlife diseases. Trends Ecol Evol. 2007;22: 95–102.
    Brazil M. Birds of east Asia: China, Taiwan, Korea, Japan, and Russia. Princeton, New Jersey: Princeton University Press; 2009.
    Campbell TW. Avian hematology and cytology. 2nd ed. Ames, IA: Iowa State University Press; 1995.
    Chakarov N, Boerner M, Krüger O. Fitness in common buzzards at the cross-point of opposite melanin–parasite interactions. Funct Ecol. 2008;22: 1062–9.
    Chanarin I. Hematology: principles and procedures. J Clin Pathol. 1984;37: 1419.
    Chatelain M, Gasparini J, Frantz A. Do trace metals select for darker birds in urban areas? An experimental exposure to lead and zinc. Glob Chang Biol. 2016;22: 2380–91.
    Chatelain M, Gasparini J, Jacquin L, Frantz A. The adaptive function of melanin-based plumage coloration to trace metals. Biol Lett. 2014;10: 20140164.
    Chatelain M, Pessato A, Frantz A, Gasparini J, Leclaire S. Do trace metals influence visual signals? Effects of trace metals on iridescent and melanic feather colouration in the feral pigeon. Oikos. 2017;126: 1542–53.
    Chedad A, Bendjoudi D, Beladis I, Guezoul O, Chenchouni H. A comprehensive monograph on the ecology and distribution of the House bunting (Emberiza sahari) in Algeria. Front Biogeogr. 2021;13: e47727.
    Chenchouni H. Contribution à l'étude de la bio-écologie de la Cigogne blanche (Ciconia ciconia) dans la région de Batna (Nord-est algérien). Doctoral Thesis. Algeria: University of Batna; 2017a.
    Chenchouni H. Variation in White Stork (Ciconia ciconia) diet along a climatic gradient and across rural-to-urban landscapes in North Africa. Int J Biometeorol. 2017;61: 549–64.
    Clavel J, Julliard R, Devictor V. Worldwide decline of specialist species: toward a global functional homogenization? Front Ecol Environ. 2011;9: 222–8.
    Combes C. Parasitism: the ecology and evolution of intimate interactions. Chicago: University of Chicago Press; 2001.
    Comer JA, Paddock CD, Childs JE. Urban zoonoses caused by Bartonella, Coxiella, Ehrlichia, and Rickettsia species. Vector Borne Zoonotic Dis. 2001;1: 91–118.
    Corbel H, Legros A, Haussy C, Jacquin L, Gasparini J, Karimi B, Frantz A. Stress response varies with plumage colour and local habitat in feral pigeons. J Ornithol. 2016;157: 825–37.
    Côte J, Boniface A, Blanchet S, Hendry AP, Gasparini J, Jacquin L. Melanin-based coloration and host–parasite interactions under global change. Proc R Soc Lond B Biol. 2018;285: 20180285.
    Davey JW, Cezard T, Fuentes-Utrilla P, Eland C, Gharbi K, Blaxter ML. Special features of RAD Sequencing data: implications for genotyping. Mol Ecol. 2013;22: 3151–64.
    Davidsohn I, Henry JB. Clinical diagnosis by laboratory methods. 15th ed. Philadelphia, Pa: W. B. Saunders Co; 1974.
    Davis AK, Maney DL, Maerz JC. The use of leukocyte profiles to measure stress in vertebrates: a review for ecologists. Funct Ecol. 2008;22: 760–72.
    de Godoi FSL, Nishi SM, de Jesus Pena HF, Gennari SM. Toxoplasma gondii: diagnosis of experimental and natural infection in pigeons (Columba livia) by serological, biological and molecular techniques. Rev Bras Parasitol Vet. 2010;19: 238–43.
    Devictor V, Julliard R, Clavel J, Jiguet F, Lee A, Couvet D. Functional biotic homogenization of bird communities in disturbed landscapes. Glob Ecol Biogeogr. 2008a;17: 252–61.
    Devictor V, Julliard R, Couvet D, Lee A, Jiguet F. Functional homogenization effect of urbanization on bird communities. Conserv Biol. 2007;21: 741–51.
    Devictor V, Julliard R, Jiguet F. Distribution of specialist and generalist species along spatial gradients of habitat disturbance and fragmentation. Oikos. 2008b;117: 507–14.
    Dreiss A, Henry I, Ruppli C, Almasi B, Roulin A. Darker eumelanic barn owls better withstand food depletion through resistance to food deprivation and lower appetite. Oecologia. 2010;164: 65–71.
    Ducatez S, Giraudeau M, Thébaud C, Jacquin L. Colour polymorphism is associated with lower extinction risk in birds. Glob Chang Biol. 2017;23: 3030–9.
    Ducrest AL, Keller L, Roulin A. Pleiotropy in the melanocortin system, coloration and behavioural syndromes. Trends Ecol Evol. 2008;23: 502–10.
    Eck S, Fiebig J, Fiedler W, Heynen I, Nicolai B, Töpfer T, et al. Measuring birds/vögel vermessen. Germany: Deutsche Ornithologen-Gesellschaft; 2011.
    Emaresi G, Henry I, Gonzalez E, Roulin A, Bize P. Sexand melanism-specific variations in the oxidative status of adult tawny owls in response to manipulated reproductive effort. J Exp Biol. 2016;219: 73–9.
    Ermert D, Niemiec MJ, Röhm M, Glenthøj A, Borregaard N, Urban CF. Candida albicans escapes from mouse neutrophils. J Leukocyte Biol. 2013;94: 223–36.
    Evans KL, Gaston KJ, Sharp SP, McGowan A, Simeoni M, Hatchwell BJ. Effects of urbanisation on disease prevalence and age structure in blackbird Turdus merula populations. Oikos. 2009;118: 774–82.
    Fallon SM, Ricklefs RE. Parasitemia in PCR-detected Plasmodium and Haemoproteus infections in birds. J Avian Biol. 2008;39: 514–22.
    Farhi Y, Aouissi HA, Nouidjem Y, Belhamra M. Spur-winged Lapwing at Djamaa, Algeria, in June 2011. Dutch Birding. 2020;42: 186–7.
    Fokidis HB, Greiner EC, Deviche P. Interspecific variation in avian blood parasites and haematology associated with urbanization in a desert habitat. J Avian Biol. 2008;39: 300–10.
    French SS, Fokidis HB, Moore MC. Variation in stress and innate immunity in the tree lizard (Urosaurus ornatus) across an urban–rural gradient. J Comp Physiol B. 2008;178: 997–1005.
    Gaagai A, Boudoukha A, Boumezbeur A, Benaabidate L. Hydrochemical characterization of surface water in the Babar watershed (Algeria) using environmetric techniques and time series analysis. Int J River Basin Manag. 2017;15: 361–72.
    Galeotti P, Sacchi R. Differential parasitaemia in the tawny owl (Strix aluco): effects of colour morph and habitat. J Zool. 2003;261: 91–9.
    Galván I, Solano F. Melanin chemistry and the ecology of stress. Physiol Biochem Zool. 2015;88: 352–5.
    Galván I, Solano F. The evolution of euand pheomelanic traits may respond to an economy of pigments related to environmental oxidative stress. Pigment Cell Melanoma Res. 2009;22: 339–42.
    Gasparini J, Bize P, Piault R, Wakamatsu K, Blount JD, Ducrest AL, et al. Strength and cost of an induced immune response are associated with a heritable melanin-based colour trait in female tawny owls. J Anim Ecol. 2009;78: 608–16.
    George EL, Panos A. Does a high WBC count signal infection? Nursing. 2005;35: 20–1.
    Germaine SS, Rosenstock SS, Schweinsburg RE, Richardson WS. Relationships among breeding birds, habitat, and residential development in greater Tucson, Arizona. Ecol Appl. 1998;8: 680–91.
    Gilot-Fromont E, Jégo M, Bonenfant C, Gibert P, Rannou B, Klein F, et al. Immune phenotype and body condition in roe deer: individuals with high body condition have different, not stronger immunity. PLoS ONE. 2012;7: e45576.
    Godfrey PS, Toone BK, Carney MW, Flynn TG, Bottiglieri T, Laundy M, et al. Enhancement of recovery from psychiatric illness by methylfolate. Lancet. 1990;336: 392–5.
    Graczyk TK, Cranfield MR, Shiff CJ. Extraction of Haemoproteus columbae (Haemosporina: Haemoproteidae) antigen from rock dove pigeons (Columba livia) and its use in an antibody ELISA. J Parasitol. 1994;80: 713–8.
    Gregoire A, Faivre B, Heeb P, Cezilly F. A comparison of infestation patterns by Ixodes ticks in urban and rural populations of the Common Blackbird Turdus merula. Ibis. 2002;144: 640–5.
    Grimm NB, Grove JG, Pickett ST, Redman CL. Integrated approaches to long-term studies of urban ecological systems. Bioscience. 2000;50: 571–84.
    Haase E, Ito S, Sell A, Wakamatsu K. Melanin concentrations in feathers from wild and domestic pigeons. J Hered. 1992;83: 64–7.
    Hanson HE, Koussayer B, Kilvitis HJ, Schrey AW, Maddox JD, Martin LB. Epigenetic potential in native and introduced populations of house sparrows (Passer domesticus). Integr Comp Biol. 2020;60: 1458–68.
    Hart BL. Behavioural defence. In: Clayton DH, Moore J, editors. Host-parasite evolution: general principle and avian models. Oxford: Oxford University Press; 1997. p. 59–77.
    Hawkey CM, Dennett TB. A colour atlas of comparative veterinary haematology. London: Wolfe Publishing; 1989.
    Hill GE, McGraw KJ. Bird colouration: function and evolution. Cambridge: Harvard University Press; 2006.
    Ishtiaq F, Rao M, Huang X, Bensch S. Estimating prevalence of avian haemosporidians in natural populations: a comparative study on screening protocols. Parasite Vectors. 2017;10: 127.
    Jacquin L, Haussy C, Bertin C, Laroucau K, Gasparini J. Darker female pigeons transmit more specific antibodies to their eggs than do paler ones. Biol J Linn Soc. 2013a;108: 647–57.
    Jacquin L, Lenouvel P, Haussy C, Ducatez S, Gasparini J. Melanin-based coloration is related to parasite intensity and cellular immune response in an urban free living bird: the feral pigeon Columba livia. J Avian Biol. 2011;42: 11–5.
    Jacquin L, Récapet C, Bouche P, Leboucher G, Gasparini J. Melanin-based coloration reflects alternative strategies to cope with food limitation in pigeons. Behav Ecol. 2012;23: 907–15.
    Jacquin L, Récapet C, Prévot-Julliard AC, Leboucher G, Lenouvel P, Erin N, et al. A potential role for parasites in the maintenance of color polymorphism in urban birds. Oecologia. 2013b;173: 1089–99.
    Jacquin L. Coloration mélanique et stratégies d'histoire de vie chez le pigeon biset urbain. Doctoral Thesis. University of Paris 6; 2011.
    Jarry G, Baillon F. Hivernage de la tourterelle des bois (Streptopelia turtur) au Sénégal: étude d'une population dans la région de Nianing. Paris: Report of CRBPO; 1991.
    Jiguet F, Sunnen L, Prévot AC, Princé K. Urban pigeons losing toes due to human activities. Biol Conserv. 2019;240: 108241.
    Johnston RF, Janiga M. Feral pigeons. Vol. 4. Oxford: Oxford University Press; 1995.
    Karell P, Ahola K, Karstinen T, Kolunen H, Siitari H, Brommer JE. Blood parasites mediate morph-specific maintenance costs in a colour polymorphic wild bird. J Evol Biol. 2011;24: 1783–92.
    Kark S, Iwaniuk A, Schalimtzek A, Banker E. Living in the city: can anyone become an 'urban exploiter'? J Biogeogr. 2007;34: 638–51.
    Kilvitis HJ, Hanson H, Schrey AW, Martin LB. Epigenetic potential as a mechanism of phenotypic plasticity in vertebrate range expansions. Integr Comp Biol. 2017;57: 385–95.
    Kittilsen S, Schjolden J, Beitnes-Johansen I, Shaw JC, Pottinger TG, Sørensen C, et al. Melanin-based skin spots reflect stress responsiveness in salmonid fish. Horm Behav. 2009;56: 292–8.
    Kolomak IO, Berdnyk VP, Kyrychko OB, Nedosekov VV. Analysis of ultrastructural morphometric changes of pigeon kidneys affected by colibacteriosis. Transl Res Vet Sci. 2019;2: 37–49.
    Kramar DE, Carstensen B, Prisley S, Campbell J. Mercury concentrations in blood and feathers of nestling Bald Eagles in coastal and inland Virginia. Avian Res. 2019;10: 3.
    Krause ET, Krüger O, Hoffman JI. The influence of inherited plumage colour morph on morphometric traits and breeding investment in zebra finches (Taeniopygia guttata). PLoS ONE. 2017;12: e0188582.
    Krüger O, Lindström J. Lifetime reproductive success in common buzzard, Buteo buteo: from individual variation to population demography. Oikos. 2001;93: 260–73.
    Law GRJ. Blood samples from jugular vein of turkeys. Poult Sci. 1960;39: 1450–2.
    Le Viol I, Jiguet F, Brotons L, Herrando S, LindströmPearce-Higgins ÅJW, et al. More and more generalists: two decades of changes in the European avifauna. Biol Lett. 2012;8: 780–2.
    Leclaire S, Chatelain M, Pessato A, Buatois B, Frantz A, Gasparini J. Pigeon odor varies with experimental exposure to trace metal pollution. Ecotoxicology. 2019;28: 76–85.
    Luniak M. Synurbization – adaptation of animal wildlife to urban development. In: Shaw WW, Harris K, Vandruff L, editors. Proceedings of the 4th international symposium on urban wildlife conservation. Tucson, Arizona: University of Arizona; 2004. p. 50–5.
    Madans JH, Webster KM. Health surveys. In: Wright JD, editor. International encyclopedia of the social and behavioral sciences. 2nd ed. Orlando: University of Central Florida; 2015. p. 725–30.
    Martin LB. Stress and immunity in wild vertebrates: timing is everything. Gen Comp Endocrinol. 2009;163: 70–6.
    Martínez J, Vásquez RA, Venegas C, Merino S. Molecular characterisation of haemoparasites in forest birds from Robinson Crusoe Island: is the Austral Thrush a potential threat to endemic birds? Bird Conserv Int. 2015;25: 139–52.
    Martinossi-Allibert I, Clavel J, Ducatez S, Viol IL, Teplitsky C. Does habitat specialization shape the evolutionary potential of wild bird populations? J Avian Biol. 2017;48: 1158–65.
    Marzluff JM. Worldwide urbanization and its effects on birds. In: Marzluff JM, Bowman R, Donnelly R, editors. Avian ecology and conservation in an urbanizing world. Boston: Springer; 2001. p. 19–47.
    McCarren S, Sumasgutner P, Tate G, Koeslag A, Amar A. Clinal variation in the polymorphic Black Sparrowhawk Accipiter melanoleucus is unrelated to infection by the blood parasite Haemoproteus nisi. J Ornithol. 2021;162: 231–41.
    Miller LK, Brooks R. The effects of genotype, age, and social environment on male ornamentation, mating behavior, and attractiveness. Evolution. 2005;59: 2414–25.
    Møller AP. Interspecific variation in fear responses predicts urbanization in birds. Behav Ecol. 2010;21: 365–71.
    Møller AP. Successful city dwellers: a comparative study of the ecological characteristics of urban birds in the Western Palearctic. Oecologia. 2009;159: 849–58.
    Moreno J, Møller AP. Are melanin ornaments signals of antioxydant and immune capacity in birds? Acta Zool Sin. 2006;52: 202–8.
    Nebel C, Harl J, Pajot A, Weissenböck H, Amar A, Sumasgutner P. High prevalence and genetic diversity of Haemoproteus columbae (Haemosporida: Haemoproteidae) in feral pigeons Columbae livia in Cape Town. South Africa Parasitol Res. 2020;119: 447–63.
    Obukhova NY. Geographic variation of color in the synanthropic Blue Rock Pigeon. Russ J Genet. 2001;37: 649–58.
    Ouali N, Belabed BE, Chenchouni H. Modelling environment contamination with heavy metals in flathead grey mullet Mugil cephalus and upper sediments from north African coasts of the Mediterranean Sea. Sci Total Environ. 2018;639: 156–74.
    Oxnard CE. One biologist's view of morphometrics. Annu Rev Ecol Evol Syst. 1978;9: 219–41.
    Pal M, Pop P, Mahapatra A, Bhagat R, Hore U. Diversity and structure of bird assemblages along urban-rural gradient in Kolkata, India. Urban Forest Urban Green. 2019;38: 84–96.
    Parmesan C, Yohe G. A globally coherent fingerprint of climate change impacts across natural systems. Nature. 2003;421: 37–42.
    Pellegrino I, Cucco M, Calà E, Boano G, Pavia M. Plumage coloration and morphometrics of the Little Owl Athene noctua in the Western Palearctic. J Ornithol. 2020;161: 1071–81.
    Pérez JE, Nirchio M, Alfonsi C, Muñoz C. The biology of invasions: the genetic adaptation paradox. Biol Invas. 2006;8: 1115–21.
    Périquet JC. Le Pigeon: races, élevage et utilisation, reproduction, hygiène et santé. Collection Les cahiers de l'élevage, Ed. Rustica, Paris; 1998.
    Pickett ST, Cadenasso ML, Grove JM, Boone CG, Groffman PM, Irwin E, et al. Urban ecological systems: scientific foundations and a decade of progress. J Environ Manage. 2011;92: 331–62.
    Pinheiro J, Bates D, DebRoy S, Sarkar D and R Core Team. nlme: linear and nonlinear mixed effects models. R package version 3.1–131. 2017. .
    Pollack L, Ondrasek NR, Calisi R. Urban health and ecology: the promise of an avian biomonitoring tool. Curr Zool. 2017;63: 205–12.
    Quesada J, Senar JC. The role of melaninand carotenoid-based plumage coloration in nest defence in the Great Tit. Ethology. 2007;113: 640–7.
    R Core Team. R: a language and environment for statistical computing. R foundation for statistical computing. 2020. .
    Rasmussen PC, Anderton JC. Birds of south Asia: the Ripley guide: attributes and status. 1st Edn, Vol. 2. Washington and Barcelona: Smithsonian Institution and Lynx Edicions; 2005.
    Récapet C, Dauphin L, Jacquin L, Gasparini J, Prévot-Julliard AC. Eumelanin-based colouration reflects local survival of juvenile feral pigeons in an urban pigeon house. J Avian Biol. 2013;44: 583–90.
    Reyer HU, Fischer W, Steck P, Nabulon T, Kessler P. Sex-specific nest defense in house sparrows (Passer domesticus) varies with badge size of males. Behav Ecol Sociobiol. 1998;42: 93–9.
    Roulin A, Almasi B, MeichtryStier KS, Jenni L. Eumelaninand pheomelanin-based colour advertise resistance to oxidative stress in opposite ways. J Evol Biol. 2011;24: 2241–7.
    Roulin A, Altwegg R, Jensen H, Steinsland I, Schaub M. Sex-dependent selection on an autosomal melanic female ornament promotes the evolution of sex ratio bias. Ecol Lett. 2010;13: 616–26.
    Roulin A, Altwegg R. Breeding rate is associated with pheomelanism in male and with eumelanism in female barn owls. Behav Ecol. 2007;18: 563–70.
    Roulin A, Gasparini J, Bize P, Ritschard M, Richner H. Melanin-based colorations signal strategies to cope with poor and rich environments. Behav Ecol Sociobiol. 2008;62: 507–19.
    Roulin A, Jungi TW, Pfister H, Dijkstra C. Female barn owls (Tyto alba) advertise good genes. Proc R Soc Lond B Biol. 2000;267: 937–41.
    Roulin A, Riols C, Dijkstra C, Ducrest AL. Female plumage spottiness signals parasite resistance in the barn owl (Tyto alba). Behav Ecol. 2001;12: 103–10.
    Roulin A. The evolution, maintenance and adaptive function of genetic colour polymorphism in birds. Biol Rev. 2004;79: 815–48.
    Rumsfeld JS. Health status and clinical practice: when will they meet? Circulation. 2002;106: 5–7.
    Saino N, Romano M, Rubolini D, Ambrosini R, Caprioli M, Milzani A, et al. Viability is associated with melanin-based coloration in the barn swallow (Hirundo rustica). PLoS ONE. 2013;8: e60426.
    Samuel MD, Woodworth BL, Atkinson CT, Hart PJ, LaPointe DA. Avian malaria in Hawaiian forest birds: infection and population impacts across species and elevations. Ecosphere. 2015;6: 104.
    Schultz PW, Gouveia VV, Cameron LD, Tankha G, Schmuck P, Franěk M. Values and their relationship to environmental concern and conservation behavior. J Cross-Cult Psychol. 2005;36: 457–75.
    Shochat E, Warren PS, Faeth SH, McIntyre NE, Hope D. From patterns to emerging processes in mechanistic urban ecology. Trend Ecol Evol. 2006;21: 186–91.
    Sol D, Jovani R, Torres J. Geographical variation in blood parasites in feral pigeons: the role of vectors. Ecography. 2000;23: 307–14.
    Stevens RWC, Ridgway GJ. A technique for bleeding chickens from the jugular vein. Poultry Sci. 1966;45: 204–5.
    Stone KD, Prussin C, Metcalfe DD. IgE, mast cells, basophils, and eosinophils. J Allergy Clin Immunol. 2010;125: S73-80.
    Stöppler MC, Shiel WC, Credo Reference (Firm), WebMD (Firm). Webster's new world medical dictionary, 3rd ed.; Redo Reference: Boston, MA, USA; Wiley: Hoboken, NJ, USA. 2014; 480 p.
    Sumasgutner P, Rose S, Koeslag A, Amar A. Exploring the influence of urbanization on morph distribution and morph-specific breeding performance in a polymorphic African raptor. J Raptor Res. 2018;52: 19–30.
    The GIMP team. GIMP 2.8.10. 2014. .
    Tostes R, Vashist U, Scopel KKG, Massard CL, Daemon E, D'Agosto M. Plasmodium spp. and Haemoproteus spp. infection in birds of the Brazilian Atlantic Forest detected by microscopy and polymerase chain reaction. Pesq Vet Bras. 2015;35: 67–74.
    Uhm TG, Kim BS, Chung IY. Eosinophil development, regulation of eosinophil-specific genes, and role of eosinophils in the pathogenesis of asthma. Allergy Asthma Immunol Res. 2012;4: 68–79.
    Valkiūnas G, Palinauskas V, Ilgūnas M, Bukauskaitė D, Dimitrov D, Bernotienė R, et al. Molecular characterization of five widespread avian haemosporidian parasites (Haemosporida), with perspectives on the PCR-based detection of haemosporidians in wildlife. Parasitol Res. 2014;113: 2251–63.
    Van den Brink V, Dreiss AN, Roulin A. Melanin-based coloration predicts natal dispersal in the barn owl Tyto Alba. Anim Behav. 2012;84: 805–12.
    Vignieri SN, Larson JG, Hoekstra HE. The selective advantage of crypsis in mice. Evolution. 2010;64: 2153–8.
    Vlahov D, Freudenberg N, Proietti F, Ompad D, Quinn A, Nandi V, et al. Urban as a determinant of health. J Urban Health. 2007;84: 16–26.
    Wei T, Simko V. R package "corrplot": Visualization of a Correlation Matrix (Version 0.84). 2017. .
    Yeh PJ. Rapid evolution of a sexually selected trait following population establishment in a novel habitat. Evolution. 2004;58: 166–74.

Catalog

    Figures(5)  /  Tables(4)

    Article Metrics

    Article views (380) PDF downloads (7) Cited by()

    /

    DownLoad:  Full-Size Img  PowerPoint
    Return
    Return