The challenge hypothesis: behavioral ecology to neurogenomics John C. Wingfield Journal of Ornithology ISSN 2193-7192 J Ornithol DOI 10.1007/s10336-012-0857-8 1 23 Your article is protected by copyright and all rights are held exclusively by Dt. Ornithologen-Gesellschaft e.V.. This e-offprint is for personal use only and shall not be selfarchived in electronic repositories. If you wish to self-archive your work, please use the accepted author’s version for posting to your own website or your institution’s repository. You may further deposit the accepted author’s version on a funder’s repository at a funder’s request, provided it is not made publicly available until 12 months after publication. 1 23 Author's personal copy J Ornithol DOI 10.1007/s10336-012-0857-8 REVIEW The challenge hypothesis: behavioral ecology to neurogenomics John C. Wingfield Received: 8 July 2011 / Revised: 14 April 2012 / Accepted: 24 April 2012 Ó Dt. Ornithologen-Gesellschaft e.V. 2012 Abstract Male song sparrows (Melospiza melodia) are territorial year-round. However, neuroendocrine responses to simulated territorial intrusions (STI) differ between breeding (spring) and non-breeding seasons (autumn). In spring, exposure to STI leads to increases in plasma levels of luteinizing hormone and testosterone (consistent with the challenge hypothesis), but not in autumn. This suggests that there are fundamental differences in the mechanisms driving neuroendocrine responses to STI between seasons despite apparently identical behavioral responses. Recent studies have also shown that areas of the telencephalon and diencephalon involved with singing behavior and aggression express the enzymes necessary to synthesize sex steroids de novo from cholesterol. Of these, aromatase (that regulates the conversion of testosterone to estradiol) and 3b-hydroxysteroid dehydrogenase (that regulates the synthesis of biologically active steroids) are regulated seasonally, whereas receptors for sex steroids such as androgen receptor and estrogen receptor alpha and beta are not. Functional analyses indicate specific genes that may be involved in the mechanisms of differential neuroendocrine responses to aggressive interactions in different life-history stages. Microarrays were used to test the hypothesis that gene expression profiles in the hypothalamus after territorial aggression differ between the seasons. Over 150 genes were differentially expressed between spring and autumn in the control birds and 59 genes were significantly affected by STI in autumn, but only 14 genes in spring. Real-time Communicated by Cristina Miyaki. J. C. Wingfield (&) Department of Neurobiology, Physiology and Behavior, University of California, Davis, CA 95616, USA e-mail: [email protected] PCR was performed for validation, and it indicated that STI drives differential genomic responses in the hypothalamus in the breeding versus non-breeding seasons. The results suggest major underlying seasonal effects in the hypothalamus that determine the differential response upon social interaction. Keywords Challenge hypothesis Sex steroids Aggression Gene expression Territoriality Introduction The Earth has always been a changeable planet where organisms often must deal with rapid shifts in both physical and social environments. With global changes in climate, as well as different social interactions due to changed population dynamics, an overarching question is, how do organisms organize their life cycles, time components of those cycles, and synchronize them with other individuals? Clearly they use environmental signals from the physical environment and the social environment to do this (Wingfield 2008a, b). Such social interactions include male–male interactions over territories and mates that in turn are both dependent upon and regulate reproductive hormone secretions. The evolution of traits associated with hormone–behavior interactions is also receiving considerable attention in the face of global change, shifting ranges of organisms, and the resultant social interactions in novel environments (Wingfield 2008a; Duckworth 2009; Hau and Wingfeld 2011). The focus here will be on male–male interactions as they establish and defend territories in seasonal contexts and also attract mates. Aggressive behavior expressed in these contexts is a complex suite of behaviors that can be 123 Author's personal copy J Ornithol both offensive and defensive (e.g., Wingfield et al. 2005). Quantifying aggression in territorial contexts is a complex task because of the varying postures and vocalizations expressed and their intensity; see Fig. 1 for examples in the Song Sparrow, Melospiza melodia (from Wacker et al. 2008). Although a detailed analysis of these traits is possible in captive conditions where video allows the quantification of even the most subtle differences in postures and intensity, such detailed quantification in the field is impossible because birds are moving in and out of vegetative cover and are not visible for the whole study session. Thus, to quantify aggression in field conditions, we use easily quantified behavioral traits such as latency to respond to a simulated territorial intrusion (STI), where a live decoy male Song Sparrow in a cage is placed in the territory of a free-living male, and tape-recorded songs are then played through a speaker placed alongside. When the focal male responds, it is possible to record the total number of songs given during a 10 min observation period, the closest approach to the decoy, the time spent within 5 m of the decoy, and the total number of flights around the decoy (e.g., Wingfield 1985; Wingfield and Hahn 1994). In general, the behavioral results are similar in the laboratory and field, but differences can be detected, especially when investigating the effects of hormone manipulations on suites of behavioral traits that are not easy to record in field conditions (i.e., they can differ depending upon the detailed information collected). Therefore, laboratory experiments have the potential to reveal much more specific effects of hormones and their metabolites (Wacker et al. 2008), whereas field experiments assess environmental and social effects more accurately but with more general behavioral data. Fig. 1 Behavioral traits studied in the laboratory allow a completely different assessment of aggression from field studies. Different body postures used in both offensive and defensive territorial aggression can be scored, as can their intensity. This aggression can be directed specifically at another individual, often at close range (\20 cm), or indirectly in response to the presence of another individual meters away. From Wacker et al. (2008), courtesy of Elsevier Press. Drawings by Todd Sperry Endocrine and paracrine control of aggression in birds Agonistic behaviors are expressed in all phases of an individual’s life, and it is not surprising that a suite of hormonal and central nervous system paracrine secretions have been implicated in the control of aggressive behavior (e.g., Adkins-Regan 2005; Wingfield et al. 2005). In birds, as in other vertebrates, central control involves complex interactions of paracrine actions of arginine vasotocin (AVT), vasoactive intestinal peptide (VIP), and serotonin in relation to sociality and social networks in the CNS (Adkins-Regan 2005; Goodson and Evans 2004; Goodson 2005; Goodson et al. 2006, 2009). Hormonal activation by testosterone (T) or estradiol (E2) after conversion from testosterone in target cells is also important, especially in species that show marked seasonal changes in aggression, such as those that are territorial only during the breeding season (Wingfield et al. 2005; Mukai et al. 2009). In other 123 contexts, prolactin regulates parental aggression (Buntin 1996) and corticosterone can increase competition for food (Kitaysky et al. 2003). Hormonal and paracrine control of agonistic behavior may also include deactivation (inhibition) by glucocorticoids of territorial aggression and sexual aggression (e.g., Wingfield and Silverin 1986) and by the activation of submissive behavior (Leshner 1978, 1981). When expression of agonistic behavior occurs in different seasons of the year, and usually in very different contexts such as breeding and non-breeding, an important question arises: is control of, for example, seasonal expression of territorial aggression regulated by the same mechanisms, or by a completely different means? Given the well-known role of T in the regulation of aggression in relation to reproduction, it has been questioned whether control over similar aggression in the non-breeding season is also regulated by T (e.g., Wingfield and Hahn 1994; Author's personal copy J Ornithol Wingfield and Soma 2002; Wingfield et al. 2001, 2005). However, before we go on to discuss the regulation of similar behavioral suites at different times of the year and contexts, it is important to first reflect on the biological actions of T. Control of territorial aggression in seasonal contexts: what does testosterone do? There is very extensive evidence that T levels in blood are higher during the breeding season than during the nonbreeding season. Furthermore, in many socially monogamous songbirds, plasma T concentrations peak early in spring, when males arrive in breeding territories and attract mates. There is a marked decline in T to a breeding baseline during the parental phase when both males and females may feed young (Fig. 2; Wingfield et al. 1990). In species that are territorial virtually year-round, it is clear that T levels in blood generally remain below the detectability threshold of the assay (e.g., Wingfield and Hahn 1994; Fig. 2). In the rare cases in which T levels do increase in autumn, the non-breeding season, then these peaks are involved in pair formation and may actually represent the beginning of the breeding season (with a Fig. 2 Plasma testosterone levels in free-living male Song Sparrows in relation to territorial behavior. Challenges with simulated territorial intrusions (STI) indicate that males are territorial throughout the breeding season (February–August) but not during the molt in late summer. By early autumn (October) they become territorial again, and remain so (albeit with some decline in aggressive responses to STI) during the worst weather of winter. Note that although testosterone levels in blood are high and variable in the breeding season, they are below the detectability threshold of the assay in molt, autumn and winter. From Wingfield and Hahn (1994), courtesy of Academic Press (Elsevier) hiatus during most of winter, Wingfield et al. 1997). In the northwestern subspecies of Song Sparrow, M.m. morphna, males remain in territories during the post-breeding prebasic molt, but show greatly blunted aggressive responses to STI. This is concomitant with a decrease in plasma T to undetectable levels (Fig. 2). In autumn, after the molt is complete, these males become once again very responsive to STI in terms of aggressive responses, but plasma T levels remain undetectable despite levels of territoriality similar to those seen in spring (Wingfield and Hahn 1994; Fig. 2). Therefore, what regulates this autumnal territorial aggression becomes a key question. Next, it is important to discuss how T secretion is controlled (Fig. 3) and what its biological actions are. Environmental information transduced through the CNS regulates the release of gonadotropin-releasing hormone (GnRH-1), which stimulates the release of two pituitary gonadotropins: luteinizing hormone (LH) and folliclestimulating hormone (FSH). These gonadotropins circulate in the peripheral blood to the gonads, where they regulate sexual maturation and the production of sex steroids, Fig. 3 Control mechanisms for territorial aggression in birds in spring. There are three major components to the control mechanisms. First, the regulation of hormone secretion from the hypothalamopituitary-gonad (HPG) axis (shown here). This figure summarizes how sensory information, in this case social, is transduced through neurotransmitter [e.g., glutamate (NMDA)] and neuroendocrine secretions such as gonadotropin-releasing hormone (GnRH) and gonadotropin-inhibiting hormone (GnIH) into the release of the gonadotropins luteinizing hormone (LH) and follicle-stimulating hormone (FSH—not shown) from the anterior pituitary into the blood. LH circulates to the gonad, where it acts on cells that express steroidogenic enzymes to stimulate the secretion of the sex steroid hormone testosterone (T), which is in turn released into the blood. Among the many actions of T are effects on territorial aggression 123 Author's personal copy J Ornithol Fig. 4 Control mechanisms for territorial aggression in birds in spring. There are three major components to the control mechanisms. First, the regulation of hormone secretion from the hypothalamopituitary-gonad (HPG) axis (Fig. 3), then the transport of hormones such as testosterone in the blood (lines in red shown here). In birds, T circulates while bound weakly to CBG, before entering target neurons involved in the expression of territorial aggression (color figure online) particularly T in males (Fig. 3). There is now strong evidence that LH release in birds can be inhibited by the action of another neuropeptide, gonadotropin-inhibitory hormone (GnIH; e.g., Tsutsui et al. 2009). There is extensive evidence that T affects spermatogenesis, muscle hypertrophy, accessory organs such as the cloacal protuberance, some secondary sex characters (Wingfield and Farner 1993; Owens and Short 1995), provides negative feedback for GnRH and LH (Fig. 3; Wingfield et al. 2001), and activates sexual behavior and aggression in reproductive contexts. Recent evidence also suggests that T circulates in avian blood while bound with medium affinity to corticosteroidbinding globulin (Fig. 4; Swett and Breuner 2008), and thus a second level of regulation at the level of hormone transport to its target cell is possible. Once T arrives at the target cells (e.g., neurons in areas of the brain associated with territorial aggression), it enters the cell passively and can then have four fates (Fig. 5). First it can bind directly to the androgen receptor (AR), a member of the type 1 genomic receptor family, which become gene transcription factors once they are bound to T. Second, T can be converted to E2 by the enzyme aromatase. E2 can then bind to either estrogen receptor alpha (Era) or estrogen receptor beta (Erb), both of which are genomic receptors that 123 regulate gene transcription, but different genes from those regulated by AR. Third, T can be converted to 5a-dehydrotestosterone (5a-DHT), which also binds to AR and cannot be aromatized, thus enhancing the AR gene transcription pathway. Fourth, T can be converted to 5b-dihydrotestosterone, which binds to no known receptors and also cannot be aromatized, indicating a deactivation shunt. A complex system of co-repressors and co-activators of genomic steroid receptor action are also known (Fig. 5; Shibata et al. 1997; Edwards 2000). The products of gene expression may then act in concert with neuropeptides such as AVT, VIP, and others as mentioned above and in Fig. 6. It is now clear that in regions of the brain associated with the expression of agonistic behavior, neurons express all of the enzymes necessary to synthesize T de novo from cholesterol, or from the uptake of a circulating precursor such as dehydroepiandrosterone (DHEA), androstenedione, or even progesterone (Schlinger 1994; Schlinger and Brenowitz 2002; Fig. 7). It is thought that during the breeding season, the source of T acting on the brain comes from gonadal sources and transport in the blood stream, but local production of sex steroids in brain regions may still be important (Wingfield et al. 2001; Fig. 7). It should also be noted that brain nuclei associated with the songs used in territorial aggression may also change rapidly, within a day or perhaps less (Thompson et al. 2007; Thompson and Brenowitz 2009). In the non-breeding season, the gonads regress in seasonally breeding songbirds, and circulating levels of gonadotropins and T become undetectable in the assay systems employed (Fig. 2). From this perspective, an increase in T secretion in Song Sparrows in autumn would be inappropriate, because reproductive traits would be expressed at the wrong season, and effects of T that potentially promote reproductive function would reduce survival during the autumn and winter periods (Wingfield et al. 2001). Even during the breeding season, T levels do not remain at their peak for long, and there are rapid increases and declines in blood concentrations. What regulates these surges in T? The challenge hypothesis Behavioral endocrinology has many examples of ambiguous relationships of circulating hormones to expression of patterns of behavior (Adkins-Regan 2005; Ball and Balthazart 2008). A typical example in the breeding season is that circulating levels of T in many vertebrates correlate with aggression only during periods of social instability (Wingfield 1984a, b; Wingfield et al. 1990). Male–male interactions over status and access to sexually receptive females tend to increase T secretion. However, expression Author's personal copy J Ornithol Fig. 5 Control mechanisms for territorial aggression in birds in spring. There are three major components to the control mechanisms. First, the regulation of hormone secretion from the hypothalamopituitary-gonad (HPG) axis (left part of the figure), the transport of hormones such as testosterone (T) in the blood (lines in red), and the mechanisms associated with the action of the hormone in the target cell, in this case a neuron in the brain (shown here). This three-part control system for hormone secretion, transport, and effects on target organs is an important concept because it profers many points of potential regulatory mechanisms. Once T has entered a target neuron, it has four potential fates. First, it can bind directly to the androgen receptor (AR), a type 1 genomic receptor, which become gene transcription factors once they are bound to T. Second, T can be converted to estradiol (E2) by the enzyme aromatase. E2 can then bind to either estrogen receptor alpha (Era) or estrogen receptor beta (Erb), both of which are genomic receptors that regulate gene transcription, but different genes from those regulated by AR. Third, T can be converted to 5a-dihydrotestosterone (5a-DHT), which also binds to AR and cannot be aromatized, thus enhancing the AR gene transcription pathway. Fourth, T can be converted to 5b-dihydrotestosterone, which binds to no known receptors and also cannot be aromatized, indicating a deactivation shunt. A complex system of corepressors and co-activators of genomic steroid receptor action are also known (color figure online) of parental behavior in males requires that T levels decline to the reproduction baseline. Other potential costs of T at high concentrations represent a classic trade-off, with high T promoting male reproductive function but at the cost of reduced survival and reproductive success (Dufty 1989; Wingfield et al. 1990, 2001). An extensive meta-analysis within the class Aves (Hirschenhauser et al. 2003) and of over 150 vertebrates ranging from fish to mammals (Hirschenhauser and Oliveira 2006) suggests that this trade-off, especially the relationship with parental care, persists across a broad spectrum of taxa. Is it possible that although baseline levels of T are undetectable in the non-breeding season, they increase during periods of social instability and when the individual is challenged for a winter territory? STIs in the breeding season lead to increased plasma levels of LH and T in responding males (Wingfield 1985). However, although males responded to STI in autumn with similar behavior to that seen in spring, there were no increases in LH or T at this time (Wingfield and Hahn 1994). In spring, males that obtained a territory also had increased plasma levels of T compared with males in an area where territories had already been established (Wingfield 1994). In contrast in autumn, males that established a new territory had undetectable levels of LH and T (Wingfield 1994). Autumn males also did not respond to estrogen-implanted females that were sexually receptive (Wingfield and Monk 1994). Normally males exposed to sexually responsive females in the breeding season show marked increases in T secretion (e.g., Adkins-Regan 2005; Wingfield 2006). Moreover, the castration of territorial male Song Sparrows in autumn had no effect on territorial aggression in response to STI compared with sham-operated controls (Wingfield 1994). Together, these findings strongly suggest that sex steroids of gonadal origin are not required for autumnal territoriality. 123 Author's personal copy J Ornithol Fig. 6 Control mechanisms for territorial aggression in birds in spring. There are three major components to the control mechanisms. First, the regulation of hormone secretion from the hypothalamopituitary-gonad (HPG) axis (left part of the figure), the transport of hormones such as testosterone (T) in the blood (lines in red), and the mechanisms associated with action of the hormone in the target cell, in this case a neuron in the brain (central part of the figure). The net result is the regulation of territorial aggression by neural networks (right hand part of the figure). This three-part system of control of hormone secretion, transport, and effects on target organs is an important concept because it profers many points of potential regulatory mechanisms. The secretion component on the left summarizes how sensory information, in this case social, is transduced through neurotransmitter [e.g. glutamate (NMDA)] and neuroendocrine secretions such as gonadotropin-releasing hormone (GnRH) and gonadotropin-inhibiting hormone (GnIH) into the release of the gonadotropins luteinizing hormone (LH) and follicle-stimulating hormone (FSH— not shown) from the anterior pituitary into the blood. LH circulates to the gonad, where it acts on cells that express steroidogenic enzymes to stimulate the secretion of the sex steroid hormone T, which is in turn released into the blood. Local actions of T in the testis include the regulation of spermatogenesis, but it is also released into the blood in many avian species when breeding. Among the many actions of T are effects on territorial aggression and negative feedback on neuroendocrine and pituitary secretions (red lines). In birds, T circulates while bound weakly to CBG, before entering target neurons involved in the expression of territorial aggression (center of figure). Once T has entered a target neuron, it has four potential fates. First, it can bind directly to the androgen receptor (AR), a type 1 genomic receptor, which become gene transcription factors once they are bound to T. Second, T can be converted to estradiol (E2) by the enzyme aromatase. E2 can then bind to either estrogen receptor alpha (Era) or estrogen receptor beta (Erb), both of which are genomic receptors that regulate gene transcription, but different genes from those regulated by AR. Third, T can be converted to 5a-dihydrotestosterone (5a-DHT), which also binds to AR and cannot be aromatized, thus enhancing the AR gene transcription pathway. Fourth, T can be converted to 5b-dihydrotestosterone, which binds to no known receptors and also cannot be aromatized, indicating a deactivation shunt. A complex system of co-repressors and co-activators of genomic steroid receptor action are also known. The end result is regulatory action on neural networks that regulate the expression of territorial aggression. Several neurotransmitters and neuromodulators such as arginine vasotocin, vasoactive intestinal peptide (VIP), and serotonin are also involved at this level. Evidence suggests that the basic secretory, transport, and action mechanisms are conserved across vertebrates (color figure online) Testosterone and territorial aggression in the non-breeding season: problems (Wingfield and Monk 1992). However, in autumn there were some single females as well as single males holding a territory. In some cases, there were female–female pairs, male–male pairs, and up to five males and females apparently responding to STI with territorial aggression. Other Song Sparrows were ‘‘floaters,’’ apparently not associated with a specific territory. Furthermore, of the 30 % or so of the territorial pairs that were male–female in autumn, very few actually mated and bred together the next spring (Wingfield and Monk 1992). Clearly, autumnal territoriality in northwestern Song Sparrows does not appear to be Given the previous results, is territorial behavior in autumn the same as that in the breeding season in spring? Is the context of spring territoriality the same as that in autumn? Over five years of observations of individually color-banded and free-living Song Sparrows of known sex in western Washington State (USA) showed that, as predicted, 70 % of the territorial pairs in spring were male–female. The other approximately 30 % were single males without a mate 123 Author's personal copy J Ornithol Fig. 7 Control mechanisms for territorial aggression in birds in autumn. Because this is the non-breeding season for most avian species, the hypothalamo-pituitary-gonad (HPG) axis is essentially shut down, as represented on the left hand side of the figure in faded text (compared to Fig. 6, where the HPG axis is active). There is evidence for some very low level testosterone (T) secretion that maintains negative feedback (blue lines), but territorial aggression, where it occurs in the non-breeding season, can be expressed even in the absence of the gonads. However, all of the T response machinery in target cells such as neurons involved in the regulation of territorial aggression may still be fully functional (central part of the figure). In this case, specific neurons appear to be able to express all of the enzymes (CYP/HSD) needed to synthesize T and estradiol (E2) de novo from cholesterol. There is also evidence that circulating precursors to sex steroids such as dehydroepiandrosterone (DHEA), androstenedione, and even progesterone may be taken up from the blood and converted within neurons to biologically active sex steroids such as T and E2. These then have varying fates, and may bind to genomic receptors as described in Fig. 5. Neurotransmitters and neuromodulators in neuron networks involved in territorial aggression are probably also involved, as shown in Fig. 6. In this way, the major pathways regulating territorial aggression in the breeding and nonbreeding seasons may have similar or identical bases, but different points of the regulatory pathways are shut down or upregulated. Thus, similar behavioral patterns may be regulated by a conserved pathway. However, similar outcomes of behavioral regulation can be achieved by regulating diverse combinations of the components (color figure online) associated solely with breeding territories. Indeed, in early autumn, many birds moved from their breeding territory by distances of a few meters up to several 100 m to establish a winter territory. In western Washington State, Song Sparrows in autumn appear to form ‘‘alliances’’ with one or more birds that were mostly not breeding pairs, as in spring. Thus there appear to be two periods of territory formation, one in early spring prior to breeding, and a second after the molt in early autumn that is used mostly for the purposes of wintering. reproductive function, contributing to reduced reproductive success (Ketterson et al. 1996; Wingfield et al. 2001; Wingfield and Soma 2002). Experimental manipulation of T increases activity and energetic costs (Wikelski et al. 1999), may have oncogenic effects, increases injury and mortality (Dufty 1989), interferes with pair bonds, disrupts parental care in some species (Hegner and Wingfield 1987; Silverin 1980), and suppresses immune function and recovery from oxidative damage (Ketterson et al. 1992, 1996; Owen-Ashley et al. 2006, 2008; Martin et al. 2008). Furthermore, T secretion outside the breeding season would be inappropriate, as it would induce morphological and physiological effects that are normally conducive with breeding at the wrong time, in addition to the costs associated with those effects. Nonetheless, territorial aggression in non-breeding individuals that is essentially identical to that expressed in the breeding season is widespread in many organisms (Wingfield et al. 1997, 2001, 2005). Avoiding the costs of testosterone Androgens such as T regulate male reproductive function and if expressed outside the breeding season could be unnecessarily costly. Moreover, there is considerable evidence that androgens have negative effects on male 123 Author's personal copy J Ornithol Control of territorial aggression outside the breeding season becomes an important question, and if T and its metabolites 5a-dihydrotestosterone (DHT) and estradiol are involved, how do organisms avoid potential costs? Some hypotheses have been proposed (Wingfield et al. 2001; Wingfield and Soma 2002; see also Schlinger 1994; Remage-Healey et al. 2010): 1. 2. 3. Testosterone hypersensitivity hypothesis. This predicts that the brain is more sensitive to circulating sex steroid hormones in autumn. Low plasma steroid levels from nongonadal sources could support autumnal aggression. Increased hormone receptors or enzymes to enhance sex steroid hormone actions in the brain could be important mechanism. In a free-living tropical suboscine, the Spotted Antbird, Hylophylax naevioides, in Panama, mRNA for estrogen receptor (ERa) in the preoptic area and androgen receptor (AR) in the nucleus taeniae were higher in males during the nonbreeding season when plasma levels of T were lowest (Canoine et al. 2007). Both of these brain regions are involved in territorial behavior. These data are consistent with the ‘‘increased sensitivity’’ hypothesis, but it is an unlikely hypothesis in other species such as the Song Sparrow based on behavioral and neurobiological studies (see below; Wacker et al. 2010). Neurosteroid hypothesis. This predicts that the brain synthesizes steroids de novo from cholesterol (Fig. 7), so there should be high sex steroid levels in brain but not in plasma. An important follow-up question is then: how is enzyme expression in brain regulated (Schlinger 1994; Schlinger and Brenowitz 2002; Soma et al. 1999a, b; Soma et al. 2000a, b; Soma and Wingfield 2001; Pradhan et al. 2010; Remage-Healey et al. 2010; Figs. 6, 7)? Circulating precursor hypothesis. A corollary of the neurosteroid hypothesis predicts that a steroid precursor such as dehydroepiandrosterone (DHEA) is secreted into the blood from, for example, the adrenal cortex, and circulates to the brain or other target tissues, where it is taken up by specific cells and converted to biologically active steroids such as T, DHT, and E2 (Soma and Wingfield 2001; Soma et al. 2002; Wingfield and Soma 2002; Remage-Healey et al. 2010; Fig. 7). These hypotheses are not mutually exclusive, and different ones or combinations of them may be prevalent in different species, suggesting that control of territoriality may have evolved numerous times in different contexts and life-history stages (e.g., Wingfield and Soma 2002; AdkinsRegan 2005; Hau and Wingfeld 2011). We now turn our focus to control of territoriality in the Song Sparrow, where we compare breeding and non-breeding life-history stages. 123 Testosterone and territorial aggression in the non-breeding season: regulation of neural steroids in Song Sparrows Evidence from several vertebrate taxa clearly indicate that enzymes in neurons convert T to E2, metabolize circulating precursors such as DHEA (resulting in both T and E2), or even synthesize sex steroids de novo from cholesterol (Schlinger 1994; Schlinger and Brenowitz 2002; Soma et al. 2002; Wingfield and Soma 2002; Remage-Healey et al. 2010; Figs. 6, 7). The production of sex steroid hormones locally in brain regions associated with the expression of territorial aggression could be a powerful way to avoid high circulating levels, such as those from gonadal sources, which would then activate a morphology and physiology typical of reproductive function and also influence the expression of sexual behavior at the wrong time (Wingfield and Soma 2002). For local neural production of sex steroids to be effective, those tissues should also express androgen receptors (AR) that bind T and or DHT, and E2 receptors (ERa or ERb types). These in turn influence the transcription of different genes, thus determining patterns of behavior without affecting other regions of the brain or peripheral tissues that in spring would be responding to widespread sex hormone secretion from gonadal tissue broadcast through the blood circulation (Fig. 3). Local neural expression of specific steroidmetabolizing enzymes, the ability to take up circulating steroid hormone precursors that are otherwise biologically inactive and convert them to active steroids, plus the potential regulation of AR and ER types to affect sensitivity to those locally produced steroids, provide unprecedented flexibility in how a neuron responds to a hormone signal! AR appears to be particularly important for prebreeding territorial behavior, but less so later in the breeding season (Sperry et al. 2010), whereas ERs may be more important in the non-breeding season (Soma et al. 1999b). More work is needed to tease apart potential differences in neuron responses to steroid hormones in different seasons. Whereas the hypothalamo-pituitary-gonad axis is activated in the breeding season, resulting in a cascade of gonadotropin-releasing hormone expression, pituitary release of the gonadotropins LH and follicle-stimulating hormone (FSH), and thus gonadal development, and the secretion of sex steroid hormones which then regulate essentially all aspects of territorial aggression in reproductive contexts, this axis appears to be completely inactive in the non-breeding season (e.g., Dawson et al. 2001; Wingfield and Silverin 2002, 2009; Bentley et al. 2007; Fig. 7). How, then, is autumn territoriality regulated, and more importantly, what aspect of the local neural steroidmetabolizing system is controlled? Ways in which this Author's personal copy J Ornithol could be achieved include changing enzyme expression and activities, regulating the circulating levels of steroid hormone precursors such as DHEA, and the differential expression of steroid hormone receptors such as AR and ERs in local brain regions. Again, each possibility is not mutually exclusive, and combinations of changes are possible. Key enzymes whose expression and activity in local brain regions could be regulated include 3b-hydroxysteroid dehydrogenase (3b-HSD), which is essential for biological activity; aromatase that is responsible for the conversion of testosterone to estradiol thus favoring ERa and ERb actions: 5a-reductase mediating the conversion of testosterone to 5a-DHT that cannot be aromatized thus favoring AR actions; and 5b-reductase that is a de-activation shunt converting testosterone to 5b-DHT that apparently does not bind to any known genomic receptor (Schlinger 1994; Schlinger and Brenowitz 2002; Wingfield and Soma 2002; Figs. 5, 6). There is growing evidence that the expression of some of these enzymes in local regions of the brain occurs seasonally (e.g., Schlinger and Brenowitz 2002; Soma 2006; Remage-Healey et al. 2010; Wacker et al. 2010), including in the Song Sparrow males that activate territorial aggression in the autumn (Soma and Wingfield 2003; Pradhan et al. 2010). The enzymes 3b-HSD, aromatase, and others do appear to be regulated—but how? In spring, but not in autumn, STI results in increases in LH and T. However, male Song Sparrows captured after STI in autumn had increased 3b-HSD activity in the central medial and caudal telencephalon compared with controls (Pradhan et al. 2010). Thus, it appears that although circulating biologically active sex steroids appear to be absent in the autumn, the brain not only makes its own sex steroids by activating enzymes in specific brain regions, but this enzymatic activity is regulated by social stimuli. Mechanisms of this regulation remain to be determined. Other ways in which costs of circulating T in the nonbreeding season could be avoided involve the regulation of steroid hormone precursors such as DHEA. The most probable source of DHEA is the adrenal cortical cells (Schlinger et al. 2008). Circulating DHEA levels are modulated with season: they are low during molt, when territorial aggression is also at a nadir, and high during breeding and again in autumn when territorial aggression is elevated (Soma and Wingfield 2001; Soma et al. 2002). Furthermore, implanting DHEA in autumn enhanced singing behavior and produced morphological effects that increased song control regions, HVC (Soma et al. 2002). Thus, an increase in plasma levels of DHEA from molt to autumn could result in more substrate for conversion to T and/or E2, thereby activating autumnal territoriality (Fig. 7). However, it is unclear how seasonal changes in DHEA release are regulated, but it apparently does not involve the hypothalamo-pituitary-adrenal axis or the HPG axis (Soma et al. 2002). As discussed earlier, yet another way to adjust control mechanisms for autumn territorial behavior is to regulate the expression of AR and ERs. In male Spotted Antbirds, ERa and AR are upregulated in local brain regions during the non-breeding season (Canoine et al. 2007) consistent with the T hypersensitivity hypothesis. Note that this does not appear to be the case in male Song Sparrows in autumn (Wacker et al. 2010), where AR is lower than in the breeding season and ERa and ERb do not appear to change. These disparate results suggest a ‘‘diversity of mechanisms’’ by which autumn territoriality and its regulation evolved. Such diversity and the potential trade-offs may be widespread in endocrine and neuroendocrine control systems (Hau and Wingfeld 2011). Challenge hypothesis revisited Returning to the original hypothesis, social instability as males compete for territories and mates results in increases in LH and T, especially in those species in which males show extensive parental care (Wingfield et al. 1990; Hirschenhauser et al. 2003; Lynn et al. 2005). Nonetheless, because the HPG axis appears to be inactive in the nonbreeding season, STI fails to raise LH or T levels in male Song Sparrows in autumn despite a very similar behavioral response (Wingfield and Hahn 1994). However, STI in male Song Sparrows in autumn does result in an increase in 3b-HSD activity in telencephalic areas associated with territorial aggression. This activity required the presence of co-factors such as NAD? (Pradhan et al. 2010). Such a remarkable finding suggests that the challenge hypothesis is still valid in the non-breeding season, but instead of activating the classic HPG axis and peripheral levels of T, local enzyme activity in the brain is activated to produce sex steroids locally, thus avoiding peripheral effects and potential costs (Pradhan et al. 2010; Fig. 7). Such mechanisms may enable the social modulation of sex steroid production locally in many other contexts and species, and further research is needed to explore these possibilities. The neural and neuroendocrine mechanisms of this reflex, the social modulation of T, in spring (when breeding) remain a mystery. Because the same behavioral interactions in autumn do not result in an increase in LH and T, then the hypothalamic activity of autumn birds will be an important control for hypothalamic activity in spring in response to STIs. We collected hypothalami from freeliving male Song Sparrows exposed to STI and from control males in spring and autumn, and subjected the RNA extract to microarray analysis (Mukai et al. 2009). The cDNA microarray contained about 18,000 genes from the 123 Author's personal copy J Ornithol Zebra Finch brain when a pooled Zebra Finch sample was used as a reference. Although several hundred genes were either upregulated or downregulated in relation to treatments, ingenuity pathway analysis revealed certain candidates that may be involved in the neuroendocrine pathway leading to LH release in spring (Mukai et al. 2009). Validation of the microarray results by real-time PCR showed that the expression of glycoprotein hormones alpha chain precursor (CGA) and transthyretin (TTR) were upregulated in spring. Results were calculated in terms of relative amounts of RNA using b-actin as an internal control, and expressed as the mean fold-change to group with the lowest expression value. Both CGA and TTR have been shown to be important mediators of photoperiod effects on GnRH and LH release in Japanese Quail, Coturnix japonica (e.g., Yoshimura 2004; Watanabe et al. 2007). It is now possible that these genes may also be involved in mediating social effects on GnRH as well. Further work on transcriptomics will be illuminating. Conclusions and future research Testosterone and its metabolites DHT and E2 regulate several behavioral traits associated with territorial aggression. The context of aggression in autumn Song Sparrows is different from that in spring. Testosterone and E2 appear to be involved in autumnal aggression, although circulating levels are not important. The mechanisms by which the T message gets to the brain vary with season, with neural steroid production predominating in the non-breeding season (Figs. 3, 4, 5, 6, 7). The neural and neuroendocrine pathways that mediate the social modulation of T in spring (breeding) do not appear to be functional in autumn. Brain enzyme activity in autumn is socially modulated, and may avoid the costs of high circulating blood sex steroids in the non-breeding season. Territorial aggression is a complex suite of traits. It is not surprising, then, that when behavior is studied in increasing detail, even more potentially complex regulatory pathways emerge (Wacker et al. 2008). In laboratory studies that performed a detailed analysis of aggressive behavioral traits in response to STI, it was demonstrated that the aromatase inhibitor fadrozole did not inhibit nonbreeding season aggression in every aspect (as shown in Fig. 1), compared with much broader observations of the number of songs, closest approach, etc., made in the field (Wacker et al. 2008). These data suggest that more detailed analysis may reveal some traits regulated by ER pathways and others regulated by AR pathways (see also Sperry et al. 2010). Furthermore, the possible role of potential neuromodulatory peptides such as VIP can also be determined now (Wacker et al. 2008). Future studies will be 123 particularly interesting, as they can take advantage of the rich diversity of patterns of territoriality in birds and begin to tease apart intriguing mechanisms, as well as the diversity of these mechanisms, by which different components of an otherwise highly conserved hormone system may be adjusted in different contexts (Hau and Wingfeld 2011). Behavioral ecology, evolutionary biology, and mechanistic approaches at the neural and endocrine levels mesh together well. This diversity of mechanisms illustrates how organisms manage state transitions in their life cycles in ways that we could not have imagined. The future use of genomic, proteomic and bioinformatics approaches will allow us to integrate behavioral ecology, evolutionary biology, and cell/molecular mechanisms (organism–environment interactions), and will allow even more powerful analyses. Acknowledgments JCW is grateful to the National Science Foundation for a series of grants that have supported much of the research and ideas discussed in this manuscript. The most current grant is IOS0750540. He also acknowledges support from the Russell F. Stark Professorship from the University of Washington and the Endowed Chair in Physiology, University of California, Davis. The author is also grateful to the following people who worked on this project over the past 30 years: Lee B. Astheimer, Gregory F. Ball, Eliot Brenowitz, D. Shallin Busch, William Buttemer, David Clayton, Alfred M. Dufty Jr., Wolfgang Goymann, Thomas P. Hahn, Michaela Hau, Robert Hegner, Kathleen Hunt, Meta Landys, Sharon Lynn, Simone Meddle, Ignacio Moore, Michael C. Moore. Motoko Mukai, Devleena S. Pradhan, Marilyn Ramenofsky, Kiran Soma, Barney Schlinger, Todd Sperry, Douglas Wacker, Gang Wang, and Martin Wikelski. Their contributions were invaluable. References Adkins-Regan E (2005) Hormones and animal social behavior. Princeton University Press, Princeton Ball GF, Balthazart J (2008) Individual variation and the endocrine regulation of behavior and physiology in birds: a cellular/ molecular perspective. Phil Trans R Soc B 363:1699–1710 Bentley GE, Tsutsui K, Wingfield JC (2007) Endocrinology of reproduction. In: Jamieson BGM (eds) Reproductive biology and phylogeny of Aves (birds). Science, Enfield, pp 181–242 Buntin JD (1996) Neural and hormonal control of parental behavior in birds. Adv Study Behav 25:161–213 Canoine V, Fusani L, Schlinger BA, Hau M (2007) Low sex steroids, high steroid receptors: increasing the sensitivity of the nonreproductive brain. J Neurobiol 67:57–67 Dawson A, King VM, Bentley GE, Ball GF (2001) Photoperiodic control of seasonality in birds. J Biol Rhythms 16:365–380 Duckworth RA (2009) The role of behavior in evolution: a search for mechanism. Evol Ecol 23:513–531 Dufty AM (1989) Testosterone and survival. Horm Behav 23:185–193 Edwards DP (2000) The role of coactivators and corepressors in the biology and mechanism of action of steroid hormone receptors. J Mamm Gland Biol Neoplasia 5:307–324 Goodson JL (2005) The vertebrate social behavior network: evolutionary themes and variations. Horm Behav 48:11–22 Author's personal copy J Ornithol Goodson JL, Evans AK (2004) Neural responses to territorial challenge and nonsocial stress in male song sparrows: segregation, integration, and modulation by a vasopressin V1 antagonist. Horm Behav 46:371–381 Goodson JL, Evans AK, Wang Y (2006) Neuropeptide binding reflects convergent and divergent evolution in species-typical group sizes. Horm Behav 50:223–236 Goodson JL, Schrock SE, Klatt JD, Kabelik D, Kingsbury MA (2009) Mesotocin and nonapeptide receptors promote estrildid flocking behavior. Science 235:862–865 Hau M, Wingfeld JC (2011) Hormonally-regulated trade-offs: evolutionary variability and phenotypic plasticity in testosterone signaling pathways. In: Flatt T, Heyland A (eds) Mechanisms of life history evolution. Oxford University Press, Oxford Hegner RE, Wingfield JC (1987) Effects of experimental manipulation of testosterone levels on parental investment and breeding success in male house sparrows. Auk 104:462–469 Hirschenhauser K, Oliveira RF (2006) Social modulation of androgens in males vertebrates: meta-analyses of the challenge hypothesis. Anim Behav 71:265–277 Hirschenhauser K, Winkler H, Oliveira RF (2003) Comparative analysis of male androgen responsiveness to social environment in birds: the effects of mating system and paternal incubation. Horm Behav 43:508–519 Ketterson ED, Nolan V Jr, Wolf L, Ziegenfus C (1992) Testosterone and avian life histories: effects of experimentally elevated testosterone on behavior and correlates of fitness in the darkeyed junco (Junco hyemalis). Am Nat 140:980–999 Ketterson ED, Nolan V Jr, Cawthorn MJ, Parker PG, Ziegenfus C (1996) Phenotypic engineering: using hormones to explore the mechanistic and functional bases of phenotypic variation in nature. Ibis 138:70–86 Kitaysky AS, Kitaiskaia EV, Piatt JF, Wingfield JC (2003) Benefits and costs of increased levels of corticosterone in seabird chicks. Horm Behav 43:140–149 Leshner AI (1978) An introduction to behavioral endocrinology. Oxford University Press, New York Leshner AI (1981) The role of hormones in the control of submissiveness. In: Brain PF, Denton D (eds) Multidisciplinary approaches to aggression research. Elsevier, Amsterdam, pp 302–322 Lynn SE, Walker BG, Wingfield JC (2005) A phylogenetically controlled test of hypotheses for behavioral insensitivity to testosterone in birds. Horm Behav 47:170–177 Martin LB, Weil ZM, Nelson RJ (2008) Seasonal changes in vertebrate immune activity: mediation by physiological tradeoffs. Phil Trans R Soc Lond B 363:321–339 Mukai M, Replogle K, Drnevich J, Wang G, Wacker D, Band M, Clayton DF, Wingfield JC (2009) Seasonal differences of gene expression profiles in song sparrow (Melospiza melodia) hypothalamus in relation to territorial aggression. PLoS ONE 4(12):e8182 Owen-Ashley NT, Turner M, Hahn TP, Wingfield JC (2006) Hormonal, behavioral, and thermoregulatory responses to bacterial lipopolysaccharide in captive and free-living whitecrowned sparrows (Zonotrichia leucophrys gambelii). Horm Behav 49:15–19 Owen-Ashley NT, Hasselquist D, Råberg L, Wingfield JC (2008) Latitudinal variation of immune defense and sickness behavior in the white-crowned sparrow (Zonotrichia leucophrys). Brain Behav Immun 22:614–625 Owens IPF, Short RV (1995) Hormonal basis of sexual dimorphism in birds: implications for new theories of sexual selection. Trends Ecol Evol 10:44–47 Pradhan DS, Newman AEM, Wacker DW, Wingfield JC, Schlinger BA, Soma KK (2010) Aggressive interactions rapidly increase androgen synthesis in the brain during the non-breeding season. Horm Behav 57:381–389 Remage-Healey L, London SE, Schlinger BA (2010) Birdsong and the neural production of steroids. J Chem Neuroanat 39:72–81 Schlinger BA (1994) Estrogens to song: picograms to sonograms. Horm Behav 28:191–198 Schlinger BA, Brenowitz EA (2002) Neural and hormonal control of birdsong. In: Pfaff D et al (eds) Hormones, brain and behavior, vol 2. Elsevier, Amsterdam, pp 799–839 Schlinger BA, Pradhan DS, Soma KK (2008) 3-HSD activates DHEA in the songbird brain. Neurochem Int 52:611–620 Shibata H, Spencer TE, Oñate SA, Jenster G, Tsai SY, O’Malley BW (1997) Role of co-activators and co-repressors in the mechanism of steroid/thyroid receptor action. Rec Prog Horm Res 52:141–164 Silverin B (1980) Effects of long-acting testosterone treatment on free-living pied flycatchers, Ficedula hypoleuca, during the breeding period. Anim Behav 28:906–912 Soma K (2006) Testosterone and aggression: Berthold, birds and beyond. J Neuroendocrinol 18:543–551 Soma KK, Wingfield JC (2001) Dehydroepiandrosterone in songbird plasma: seasonal regulation and relationship to territorial aggression. Gen Comp Endocrinol 123:144–155 Soma KK, Wingfield JC (2003) Brain aromatase, 5a-reductase, and 5b-reductase change seasonally in wild male song sparrows: relationship to territorial aggression. J Neurobiol 56:209–221 Soma KK, Bindra R, Gee J, Wingfield J, Schlinger B (1999a) Androgen-metabolizing enzymes show region-specific changes across the breeding season in the brain of a wild songbird. J Neurobiol 41:176–188 Soma KK, Sullivan K, Wingfield JC (1999b) Combined aromatase inhibitor and antiandrogen treatment decreases territorial aggression in a wild songbird during the non-breeding season. Gen Comp Endocrinol 115:442–453 Soma KK, Sullivan KA, Tramontin AD, Saldanha CJ, Schlinger BA, Wingfield JC (2000a) Acute and chronic effects of an aromatase inhibitor on territorial aggression in breeding and non-breeding male song sparrows. J Comp Physiol A 186:759–769 Soma KK, Tramontin AD, Wingfield JC (2000b) Oestrogen regulates male aggression in the non-breeding season. Proc R Soc Lond Ser B 267:1089–1096 Soma KK, Wissman AM, Brenowitz EA, Wingfield JC (2002) Dehydroepiandrosterone (DHEA) increases male aggression and the size of an associated brain region. Horm Behav 41:203–212 Sperry TS, Wacker DW, Wingfield JC (2010) The role of androgen receptors in regulating territorial aggression in male song sparrows. Horm Behav 57:86–95 Swett MB, Breuner CW (2008) Interaction of testosterone, corticosterone and corticosterone-binding globulin in the white-throated sparrow (Zonotrichia albicollis). Comp Biochem Physiol A Mol Integr Physiol 151:226–231 Thompson CK, Brenowitz E (2009) Neurogenesis in an adult avian song nucleus is reduced by decreasing caspase-mediated apoptosis. J Neurosci 29:4586–4591 Thompson CK, Bentley GE, Brenowitz E (2007) Rapid seasonal-like regression of the adult avian song control system. Proc Nat Acad Sci USA104:15520–15525 Tsutsui K, Saigoh E, Yin H, Ubuka T, Chowdhury VS, Osugi T, Ukena K, Sharp PJ, Wingfield JC, Bentley GE (2009) A new key hormone controlling reproduction, gonadotrophin-inhibitory hormone in birds: discovery, progress and prospects. J Neuroendocrinol 21:271–275 Wacker DW, Schlinger BA, Wingfield JC (2008) Combined effects of DHEA and fadrozole on aggression and neural VIP immunoreactivity in the non-breeding male song sparrow. Horm Behav 53:287–294 123 Author's personal copy J Ornithol Wacker DW, Wingfield JC, Davis JE, Meddle SL (2010) Seasonal changes in aromatase and androgen receptor, but not estrogen receptor mRNA expression in the brain of the free-living male Song Sparrow, Melospiza melodia morphna. J Comp Neurol 518:3819–3835 Watanabe T, Yamamura T, Watanabe M, Yasuo S, Nakao N, Dawson A, Ebihara S, Yoshimura T (2007) Hypothalamic expression of thyroid hormone-activating and inactivating enzyme genes in relation to photorefractoriness in birds and mammals. Am J Physiol Regul Integr Comp Physiol 292:R568–R572 Wikelski M, Lynn S, Breuner C, Wingfield JC, Kenagy GJ (1999) Energy metabolism, testosterone and corticosterone in whitecrowned sparrows. J Comp Physiol A 185:463–470 Wingfield JC (1984a) Environmental and endocrine control of reproduction in the song sparrow, Melospiza melodia. I. Temporal organization of the breeding cycle. Gen Comp Endocrinol 56:406–416 Wingfield JC (1984b) Environmental and endocrine control of reproduction in the song sparrow, Melospiza melodia. II. Agonistic interactions as environmental information stimulating secretion of testosterone. Gen Comp Endocrinol 56:417–424 Wingfield JC (1985) Short-term changes in plasma levels of hormones during establishment and defense of a breeding territory in male song sparrows, Melospiza melodia. Horm Behav 19:174–187 Wingfield JC (1994) Control of territorial aggression in a changing environment. Psychoneuroendocrinol 19:709–721 Wingfield JC (2006) Communicative behaviors, hormone-behavior interactions, and reproduction in vertebrates. In: Neill JD (ed) Physiology of reproduction. Academic Press, New York, pp 1995–2040 Wingfield JC (2008a) Comparative endocrinology, environment and global change. Gen Comp Endocrinol 157:207–216 Wingfield JC (2008b) Organization of vertebrate annual cycles: implications for control mechanisms. Phil Trans R Soc B 363:425–441 Wingfield JC, Farner DS (1993) The endocrinology of wild species. In: Farner DS, King JR, Parkes KC (eds) Avian biology, vol 9. Academic, New York, pp 163–327 123 Wingfield JC, Hahn TP (1994) Testosterone and territorial behavior in sedentary and migratory sparrows. Anim Behav 47:77–89 Wingfield JC, Monk D (1992) Control and context of year-round territorial aggression in the non-migratory song sparrow, Melospiza melodia morphna. Ornis Scand 23:298–303 Wingfield JC, Monk D (1994) Behavioral and hormonal responses of male song sparrows to estrogenized females during the nonbreeding season. Horm Behav 28:146–154 Wingfield JC, Silverin B (1986) Effects of corticosterone on territorial behavior of free-living song sparrows, Melospiza melodia. Horm Behav 20:405–417 Wingfield JC, Silverin B (2002) Ecophysiological studies of hormone-behavior relations in birds. In: Pfaff DW, Arnold AP, Etgen AM, Fahrbach SE, Rubin RT (eds) Hormones, brain and behavior, vol 2. Elsevier, Amsterdam, pp 587–647 Wingfield JC, Silverin B (2009) Ecophysiological studies of hormone–behavior relations in birds. In: Pfaff DW, Arnold AP, Etgen AM, Fahrbach SE, Rubin RT (eds) Hormones, brain and behavior, vol 2, 2nd edn. Academic, New York, pp 817–854 Wingfield JC, Soma KK (2002) Spring and autumn territoriality: same behavior different mechanisms? Integr Comp Biol 42:11–20 Wingfield JC, Hegner RE, Dufty AM Jr, Ball GF (1990) The ‘‘challenge hypothesis’’: theoretical implications for patterns of testosterone secretion, mating systems, and breeding strategies. Am Nat 136:829–846 Wingfield JC, Jacobs J, Hillgarth N (1997) Ecological constraints and the evolution of hormone–behavior interrelationships. Ann NY Acad Sci 807:22–41 Wingfield JC, Lynn SE, Soma KK (2001) Avoiding the ‘‘costs’’ of testosterone: ecological bases of hormone–behavior interactions. Brain Behav Evol 57:239–251 Wingfield JC, Moore IT, Goymann W, Wacker DW, Sperry T (2005) Contexts and ethology of vertebrate aggression: implications for the evolution of hormone–behavior interactions. In: Nelson RJ (ed) Biology of aggression. Oxford University Press, New York, pp 179–210 Yoshimura T (2004) Molecular bases for seasonal reproduction in birds. J Poultry Sci 41:251–258
© Copyright 2025 Paperzz