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Keywords:

  • body mass;
  • cost of reproduction;
  • density;
  • ovulation;
  • red deer

Summary

  1. Top of page
  2. Summary
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Supporting Information
  • 1
    In large herbivores, the timing of breeding is important for females to hit peak plant protein levels. For males, the timing of reproductive effort is important to maximize the number of females they can mate during autumn rut in competition with other males. The latter depends on when most females are ovulating, but also on how other males with a different competitive ability are timing use of their capital (fat); it may pay younger males to invest more heavily later when prime aged males are exhausted.
  • 2
    Based on estimates of body mass loss, we quantify how much timing (start, peak and end dates) of male reproductive effort during rutting varies depending on male age, density and climate as well as timing of female ovulation.
  • 3
    Ovulation in adult females was delayed by 5 days from low to high density, and ovulation was also more synchronous at high density. The starting date of decline in male body mass was only later in yearlings than among other age groups. However, at low density, peak and end dates of rut became increasingly earlier and close to peak female ovulation with increasing age up to 7 years of age. Prime-aged males matched peak effort closely with peak rate of prime-aged female ovulation, while younger males were delayed. This is consistent with the view that younger males have a better chance when the prime-aged males are becoming exhausted.
  • 4
    Apart from yearlings, male age groups were synchronized in both the starting, peak and end dates of mass decline at high density. Thus, this partly follows change in female ovulation patterns, but also suggests that competition among males decreased with increasing density due probably to lower intensity of sexual selection. The lowered sexual selection may be due not only to more synchronous female ovulation, but also increasingly female-biased sex ratios and a younger male age structure with increasing density.
  • 5
    The onset of rutting is somewhat independent of male age (apart from the youngest males), but the peak and end of rutting effort is dependent strongly upon age, density and peak female ovulation. Male rutting phenology is thus best interpreted as a compromise between hitting peak female ovulation and intensity of sexual selection.

Introduction

  1. Top of page
  2. Summary
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Supporting Information

Phenology is the study of seasonal plant and animal activity driven by environmental factors. In seasonal environments, many ecological processes occurring in animal populations are synchronized with plant phenology, such as migration, reproduction and breeding. In large herbivores, the timing of birth in spring is essential for females in order to hit peak plant protein levels to support the costs of reproduction (e.g. Festa-Bianchet 1988; Loe et al. 2005). The factors affecting timing of male reproduction in ungulates have received much less attention, but probably differ substantially from that of females. While female reproductive success is limited mainly by gestation and lactation costs, male reproductive success, especially of dimorphic species, is limited by access to mates (Clutton-Brock, Albon & Guinness 1988). For obvious reasons, in order to reproduce successfully a male needs to be available for mating in the short time window in which the female is ready to conceive (about 24 h, Clutton-Brock, Guinness & Albon 1982). However, to gain access to females is not an easy task, and may involve fighting with other males for access (Geist 1974; Clutton-Brock et al. 1979), patrolling territories (Alvarez 1993), roaring contests (McComb 1987) and tending females (Hogg 1984; Hogg & Forbes 1997; Pelletier, Hogg & Festa-Bianchet 2006). The more time that is devoted to rutting activities, the less time is available for foraging (Willisch & Ingold 2007), and prime-aged males may stop eating completely (Maher & Byers 1987; Miquelle 1990). Most polygynous herbivores are capital breeders (Jönsson 1997; Festa-Bianchet, Gaillard & Jorgenson 1998). As a consequence of these energy-consuming activities and reduced time spent feeding, males lose condition as rut precedes (e.g. Kojola 1991; Yoccoz et al. 2002; Forsyth et al. 2005; Mysterud, Solberg & Yoccoz 2005). Only one study has addressed how males of different age classes are timing their effort within a rutting season relative to female oestrus or ovulation pattern, and they found that highly competitive males match female oestrus more effectively than other males (Preston, Stevenson & Wilson 2003).

In this study of a capital breeding and highly polygynous ungulate, the red deer (Cervus elaphus), we present a joint analysis of timing of male reproductive effort assessed from body mass loss relative to female rutting phenology (ovulation). We extend a previous analysis of mass loss in males (Yoccoz et al. 2002) and ovulation in females (Langvatn et al. 2004) with an explicit quantification of the timing of mass loss and ovulation rates using threshold models to assess the phenology of rutting effort; when they start to rut, when they peak in effort and when they end rutting relative to female ovulation pattern. We test the following not mutually exclusive hypotheses.

Hypothesis 1: males track female phenology

Even though males usually initiate rutting activities well before females, it is somewhat intuitive to predict that males will use most energy when females are receptive to mating. Thus, a delay in female oestrus and ovulation will delay peak effort of males. For instance, in Soay sheep (Ovis aries), competitive males time their mate-guarding to occur close to the optimal insemination period (Preston et al. 2003). As female ovulation is delayed with increasing density, but seems not to be linked to variation in the North Atlantic Oscillation (NAO) (Langvatn et al. 2004), we expect a later phenology at high than at low density, but no effect of the NAO. Consequently, as female oestrus and ovulation will be delayed, we predict a delayed peak effort of males at high density but no NAO effect on male rutting pattern.

Hypothesis 2: age determines phenology

Young males are less likely to compete successfully in male–male combat, and paternity in polygynous species is highly skewed towards prime-aged males (e.g. Pemberton et al. 1992; Coltman et al. 2002). Younger males have a higher chance to sire later in rut, when prime-aged males are exhausted, or in species with sperm competition, due to depletion of sperm in prime-aged males (Preston et al. 2001). Indeed, several studies indicate that younger males start rutting at a later date than prime-aged males (review in Mysterud, Langvatn & Stenseth 2004), but no study has quantified how this varies with density or climate. If competition among males is high (higher sexual selection intensity), we would expect age classes (that differ in competitive ability) to be less synchronous, as younger males would have less chances for mating during peak rut. This yields the prediction that males should be more synchronous at high density, as sexual selection forces are likely to be weaker (Clutton-Brock & Parker 1992; but see Stutchbury & Morton 1995 for an alternative argument in songbirds); because female ovulation is more synchronous at high density (Langvatn et al. 2004); and because population sex ratio is probably more female-biased and male age structure younger with increasing density in these populations (due to heavy male harvest; Milner et al. 2006).

Materials and methods

  1. Top of page
  2. Summary
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Supporting Information

study area

The study area comprises large parts of the Norwegian South West coast, covering six Norwegian counties: Rogaland (number of municipalities; n = 6) and Hordaland (n = 21; termed population ‘P1’), Sogn og Fjordane (n = 23; termed population ‘P2’), Møre og Romsdal (n = 25) and Sør Trøndelag (n = 13; termed population ‘P3’) and Nord Trøndelag (n = 2; termed population ‘P4’). The island Hitra in Sør Trøndelag is termed population ‘P5’. The vegetation on the West coast of Norway is mainly in the boreo nemoral zone (Abrahamsen et al. 1977). A detailed description of the (forested) habitat (Mysterud et al. 2002) and (steep and hilly) topography (Mysterud et al. 2001a,b) is given elsewhere.

red deer data

Body mass, size and age

Male and female red deer were sampled during the annual autumn harvest 1965–2003 (e.g. Mysterud et al. 2001b; Langvatn et al. 2004). Compared to the data analysed by Yoccoz et al. (2002) on male reproductive effort, we added data from 2000 to 2003 (7821 males 1 year and older with exact body mass; thus totalling 22 414 males, Table 1). The hunting period lasts from 10 September to 15 November, covering the prerut and rut period. Assuming non-selective harvesting (see below), the effect of date of culling on (age specific) body mass will estimate (age-specific) mass loss over time (termed rutting or male effort). Until 2000 hunting was not permitted during 1 October to 10 October, which made it difficult to establish the exact start of rutting for all male age classes.

Table 1.  Overview of sample sizes per age for high- and low-density periods for red deer along the West coast of Norway
Age12345678910111213141516171819 20Sum
Males
 High density458932491980 816424247129 91 54 34 24 1014 3 5 1 1 1 2 11 674
 Low density439931901566 637384240123 89 44 25 22  7 3 4 3 1 0 3 0 10 740
 Total8988643935461453808487252180 98 59 46 1717 7 8 2 1 4 2 22 414
Females
 High density13211000 823 378259236193122110 85 88 564438252022 911294 869
 Low density11961162 885 446314243198149126 79 77 6853493524181513405 190 
 Total251721621708 824573479391271236164165124978760444024246910 059

Hunting is controlled through licences issued by local wildlife boards in each municipality. In cooperation with local wildlife boards, hunters provided mandibles from all animals shot, together with records of sex, date, locality (municipality) and body mass. Body mass is dressed mass (i.e. live mass minus head, skin, viscera, bleedable blood and metapodials). Dressed mass in hinds is about 58% of live mass (Langvatn 1977), and highly correlated (r = 0·994, n = 127) with total mass in Cervids (Wallin, Cederlund & Pehrson 1996). Age determination in calves and yearlings was based on tooth eruption patterns (Loe et al. 2004), whereas older animals were aged using annuli in the cementum of the first incisor (Hamlin et al. 2000).

Ovulation

As necessary background information of timing of female breeding, we also use data on ovulation that have been analysed in detail (Langvatn et al. 2004). Data (n = 10 073) derive from the same source as the body mass data. Reproductive history of individual females can be estimated post mortem based on inspection of ovaries (Harrison & Weir 1977; Langvatn 1992). Ovulation can be assessed based on recording of a primary corpus luteum. As females are also harvested at different stages of the reproductive cycle during autumn, the presence of a primary corpus luteum regressed on the date of harvest can be used to describe temporal variation in timing of ovulation (cf. Langvatn et al. 2004 for details), which we refer to here as female phenology.

Population density

As an index for local density, we used total harvest (number of deer shot) in a municipality divided by the area of red deer habitat, as approved by the management authorities (Mysterud et al. 2001c; Mysterud et al. 2002). During the study period, the red deer population has been increasing steadily. The harvest has increased 10-fold (Statistics Norway 2004) and the number of deer killed in traffic has also increased, even after accounting for increase in traffic (Mysterud 2004). We have found recently a close correlation between harvest size and independent indices of population size, such as the number of deer seen and population size estimated with cohort analysis (Mysterud et al. 2007). This index of density also includes a spatial component, and may thus be affected potentially by habitat quality if resource levels for the same density differ. If such an effect was strong, it would probably yield a non-linear relationship between mass and density (or a poor fit). It emerged that the relationship between body mass and the density index was curvilinear if data from the municipality Eid were included. There were very few data from Eid, except from 2001 to 2003 (482 males and 379 females 1 year or older; only 27 individuals earlier than 2001). The deer harvested in Eid are mainly migrating deer shot on the way from their summer to winter ranges (Vebjørn Veiberg, personal communication). The density index for these deer may therefore be artificially high compared to the real densities they experience in their summer and winter areas. When excluding data from Eid, the relationship between body mass and the density index did not deviate from linearity. We thus excluded data from Eid in all analyses.

Other covariates

As an index of global winter climate, we used the NAO (Hurrell 1995; Hurrell et al. 2003), which is known to have a strong impact of the life history of red deer along the South West coast of Norway (Mysterud et al. 2001b; Pettorelli et al. 2005). Because the data on body mass and ovulation cover a large area, and because not all subareas are sampled each year, it is important to control for factors with a known effect on body mass in order to avoid biased estimates. Several spatial covariates were therefore considered, including distance from the coast, degree of latitude, proportion of high altitude habitat and diversity of altitudes and aspects (Mysterud et al. 2001a).

statistical analyses

To estimate objectively the start of mass loss, peak of mass loss and end dates of mass loss, we applied threshold models (Ulm 1989; for an application see Lambin & Yoccoz 2001) with one or two breaking points (φ1, or φ1 and φ2 when φ2 was estimable) on the predicted body mass from generalized additive model (GAM) fits (Hastie & Tibshirani 1990). Additive models were fitted using thin plate regression splines in the r library mgcv (Wood 2006; R Development Core Team 2007). Threshold breaks were discrete, as the covariate is Julian date. We did not aim here at finding a set of best models, as is conducted in other selection procedures, but simply at finding dates of changing slopes. For that reason, we considered only linear terms and did not attempt to fit models of higher order polynomial. The overall body mass loss of males before, during and after the rut was assessed by slopes of each segment of the piecewise regression. We replicated the same analysis on ovulation rates adjusting piecewise linear regressions of date on the predicted evolution of ovulation rate over time. We used piecewise regressions as a convenient tool for describing variation over time. Note, however, that for reading out predictions on proportions breeding, this requires logistic transformation (see Langvatn et al. 2004). We repeated this procedure of date estimation for each age class and for two density and NAO levels (greater or smaller than the study median) both for males and females.

Results

  1. Top of page
  2. Summary
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Supporting Information

Adult females delayed start of ovulation by c. 5 days from low to high population density (Langvatn et al. 2004), implying a delay in the date of maximum ovulation rate at high compared to low density (Fig. 1; Table 2). Females also ovulated more synchronously at high than low density. In support of Hypothesis 1, that males track female phenology, peak body mass decline of all males older than 2 years were matching peak female ovulation at high density, but at low density only the prime-aged males did so (Fig. 1a; Table 2). At low density, both peak and end dates as well as total male effort over a rutting season (i.e. whole mass loss based on slope estimates, Table 3) were progressively earlier by increasing age (both absolutely and relatively, except for the very oldest ages classes; see Yoccoz et al. 2002). In contrast, starting dates of mass decline were similar in males 3 years or older and independent of density (but note that overall mass loss differs depending on density; Yoccoz et al. 2002). At low density, male age groups were thus less synchronized in the peak and end dates of mass decline than at high density (Fig. 1), in support of Hypothesis 2. Indeed, at high density male age classes varied less with respect to timing of rutting effort and the observed sequence observed from young to old deer vanished (Fig. 1b; Table 3). As for female ovulation (Langvatn et al. 2004; Fig. 1), male body mass decline was not affected significantly by the NAO (Table 4), also in support of our Hypothesis 1. The GAM model with age class and date of harvest and their interaction explained 74% of the variance in body mass. The fit of the data to the model are presented in Fig. 2. The reported patterns were qualitatively consistent when analysis was replicated based only on population P3 (with most data), suggesting that temporal density dependence is operating (see Appendix SI in Supplementary material).

image

Figure 1. Timing of male body mass decline and female ovulation at (a) low and (b) high density (relative to the median: 0·844 deer shot per km2‘deer habitat’). The six age categories for males are 1, 2, 3, 4, 5–7 and > 7 years, while the three female age categories are 1, 2 and 3–13 years. Dates for male mass loss and female ovulation were defined by the same threshold methods (see Methods). The vertical solid and dotted lines refer to peak and start/end dates of ovulation for females aged 3–13 years. The colour depth of the grey shaded bars refers to level of mass loss or ovulation rate. We provide bands for start (green), peak (red) and end (blue) of rutting. For some categories, we found no ‘end dates’ within the time span covered by our sampled material (until 15 November). The box surrounding bars represents the 95% confidence interval of the estimated dates.

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Table 2.  Timing of female ovulation at low and high density (relative to the median population density: 0·844 deer shot per km2 of deer habitat). The three female age categories are 1, 2 and 3–13 years. For yearlings, we found no end dates within the time-span covered by our sampled material (until 15 November)
Age classStart date (95% CI)Max rate date (95% CI)End date (95% CI)Duration (days)
Yearlings
 Low8 Oct (5 Oct; 10 Oct)25 Oct (22 Oct; 28 Oct)
 High8 Oct (3 Oct; 11 Oct)27 Oct (23 Oct; 30 Oct)
2 years old
 Low7 Oct (6 Oct; 8 Oct)20 Oct (18 Oct; 22 Oct)25 Oct (21 Oct; 28 Oct)24
 High13 Oct (11 Oct; 14 Oct)23 Oct (21 Oct; 24 Oct)2 Nov (31 Oct; 4 Nov)20
3–13 years old
 Low2 Oct (30 Sept; 3 Oct)17 Oct (15 Oct; 18 Oct)29 Oct (27 Oct; 31 Oct)27
 High8 Oct (7 Oct; 9 Oct)16 Oct (14 Oct; 17 Oct)27 Oct (26 Oct; 28 Oct)20
Table 3.  Development of male body mass before, during and after main rut in six age classes at high and low density. For each age class there is a linear increase in body mass (Slope1) before a date (Threshold date1), where body mass starts to drop (at the rate given in Slope2). Threshold date1 reflects the date where each age class starts to rut. In some age classes there is a second threshold (Threshold date2), where mass loss levels out (Slope3), i.e. the end of rut. As data after 15 November are scarce the second threshold is not detected in all age classes. Max refers to peak of rut. We repeated this procedure for high (above median) and low (below median) density and calculated the difference in slopes and threshold dates (low density–high density estimates). A positive difference in Slope1 indicates less growth at high than low density prior to the most intensive rutting period. Negative differences between threshold dates indicate a delay in onset of rut at high compared to low density. Note that Slope2 is less steep for the two youngest compared to older age classes, indicating little investment in rutting activities. Tabulated values are real estimates multiplied by 100
Age classSlope1Threshold date1 (95% CI)Slope2Threshold date2 (95% CI)Slope3Max (95% CI)
Yearlings
 Low density0·05113 Oct–0·102
 High density0·01513 Oct–0·064
 Difference(L–H)0·036(–72·2%)0 day–0·036 (+36·3%)– 
2 years old
 Low density0·0847 Oct(5 Oct; 10 Oct)–0·174
 High density0·06211 Oct(9 Oct; 13 Oct)–0·1368 Nov(5 Nov; 11 Nov)25 Oct(21 Oct; 28 Oct)
 Difference(L–H)0·021(–25·7%)–4 days–0·038(+21·7%) 
3 years old
 Low density0·0796 Oct(3 Oct; 7 Oct)–0·4168 Nov(6 Nov; 10 Nov)27 Oct(24 Oct; 3 Nov)
 High density0·1116 Oct(4 Oct; 7 Oct)–0·4308 Nov(6 Nov; 10 Nov)–0·10222 Oct(19 Oct; 23 Oct)
 Difference(L–H)0·031(–28·7%)0 day0·013(–3·2%)0 day5 days
4 years old
 Low density–0·0937 Oct(3 Oct; 8 Oct)–0·48221 Oct(18 Oct; 23 Oct)
 High density–0·1288 Oct(6 Oct; 10 Oct)–0·51411 Nov(9 Nov; 13 Nov)–0·14224 Oct(21 Oct; 26 Oct)
 Difference(L–H)0·035(–37·7%)–1 day0·031(–6·6%)–3 days
5–7 years old
 Low density–0·2665 Oct(3 Oct; 7 Oct)–0·6894 Nov(31 Oct; 8 Nov)19 Oct(17 Oct; 20 Oct)
 High density–0·0655 Oct(4 Oct; 7 Oct)–0·6014 Nov(3 Nov; 7 Nov)–0·33421 Oct(19 Oct; 22 Oct)
 Difference(L–H)0·200(+75·4%)0 day–0·088(+12·8%)0 day–2 days
> 7 years old
 Low density–0·2478 Oct(6 Oct; 9 Oct)–0·8248 Nov(7 Nov; 10 Nov)–0·17917 Oct(13 Oct; 19 Oct)
 High density–0·1418 Oct(5 Oct; 10 Oct)–0·55031 Oct(30 Oct; 1 Nov)–0·21023 Oct(18 Oct; 28 Oct)
 Difference (L–H)0·106 (+42·9%)0 day–0·270(+39·2%)+9 days –6 days
Table 4.  Timing of male body mass decline at high and low values of the North Atlantic Oscillation (see Table 2 for definitions)
Age classStart date (95% CI)Max rate date (95% CI)End date (95% CI)Duration (days)
Yearlings
 High NAO14 Oct(8 Oct; 31 Oct)
 Low NAO12 Oct(8 Oct; 15 Oct)
2 years old
 High NAO7 Oct(5 Oct; 8 Oct)22 Oct(18 Oct; 25 Oct)
 Low NAO10 Oct(8 Oct; 11 Oct)26 Oct(22 Oct; 29 Oct)9 Nov(3 Nov; 13 Nov)31
3 years old    
 High NAO6 Oct(4 Oct; 8 Oct)21 Oct(18 Oct; 23 Oct)4 Nov(1 Nov; 6 Nov)28
 Low NAO3 Oct(1 Oct; 5 Oct)26 Oct(23 Oct; 28 Oct)10 Nov(7 Nov; 13 Nov)37
4 years old
 High NAO6 Oct(4 Oct; 8 Oct)24 Oct(21 Oct; 26 Oct)11 Nov(9 Nov; 13 Nov)35
 Low NAO7 Oct(5 Oct; 8 Oct)20 Oct(18 Oct; 21 Oct)5 Nov(2 Nov; 8 Nov)28
5–7 years old
 High NAO6 Oct(4 Oct; 7 Oct)20 Oct(18 Oct; 22 Oct)1 Nov(30 Oct; 3 Nov)25
 Low NAO3 Oct(1 Oct; 4 Oct)19 Oct(16 Oct; 21 Oct)5 Nov(2 Nov; 9 Nov)32
> 7 years old
 High NAO7 Oct(6 Oct; 9 Oct)17 Oct(12 Oct; 20 Oct)4 Nov(3 Nov; 6 Nov)27
 Low NAO4 Oct(3 Oct; 5 Oct)21 Oct(17 Oct; 26 Oct)30 Oct(28 Oct; 3 Nov)26
image

Figure 2. Generalized additive model plots of corrected body mass against date of harvesting (counting days from 1 September) for each age class. Observations were pooled with a 2-day time-step. White with grey smoothed lines show data at high and low density values are shown in black with black lines. Threshold dates are indicated with arrows: start date (green), peak date (red) and end dates (blue). Arrows at the top are high density and arrows on bottom are low density.

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Discussion

  1. Top of page
  2. Summary
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Supporting Information

The timing of breeding in strongly seasonal environments is a critical factor for reproductive success in large mammalian herbivores which, at least in females, is well documented (Clutton-Brock et al. 1982; Loison, Langvatn & Solberg 1999; Holand et al. 2006). For males of a capital breeding species (sensu Jönsson 1997), we tested the hypothesis that timing of rutting effort would be a compromise between hitting peak female ovulation on one side (potential benefit) and avoiding investment of capital (fat) at the same time as superior contestants (costs). Indeed, we found that maximal daily mass loss of males followed changes in peak female ovulation, but that rutting phenology is more synchronous among age classes at high compared to low density. This is probably a consequence of lower competition among males, and thus intensity of sexual selection. With increasing density, female ovulation is more synchronous (Langvatn et al. 2004), male age structure is younger and the sex ratio is probably more female-biased (Milner et al. 2006), all contributing to changes in sexual selection intensity (see detailed discussion below). We also highlight that start, peak and end dates of rutting among age classes were not well correlated, making the start of rutting activities, in particular, a less useful measure of total rutting effort.

Longitudinal data on reproductive tactics spanning the range of ecological conditions necessary to address the issues raised here are currently not available, although clearly such data would be preferred due to potential problems with individual heterogeneity and hunter selectivity with transversal data such as ours. Harvesting data are often a selective sample of the population yielding a potential for bias (e.g. Martínez et al. 2005; Mysterud, Tryjanowski & Panek 2006). The important point is how strong such a bias is relative to the patterns of interest. In Norway, harvesting selectivity is regulated mainly with quotas, given as calf, yearling and adults of each sex. Based on our detailed experience with the system, it is unlikely that harvesting bias, i.e. selection for phenotypic traits such as body mass, is strong within these quota categories for this time-period. The hunting tradition is for meat, not for trophies (Milner et al. 2006). Also, there are often large quotas and limited time for hunting, which reduce selectivity (Solberg et al. 2000). There is a high cost in terms of lost chances to be selective in the forested habitat along the West coast of Norway, where group size of red deer is small (average of 1·5 females per male in mixed groups during rut; Bonenfant et al. 2004). Potentially, mass loss during rut may be over-estimated if the largest males are harvested first. However, in these populations where the likelihood for a male to reach 4 years of age is < 10% (Langvatn & Loison 1999), any prime-aged male will appear very large. Thus, it is unlikely for hunters to select between a ‘small’ and a ‘large’ prime-aged stag, as in these populations prime-aged stags are so rare that if they appear and are legal to shoot, they will most probably be shot at the first encounter with a hunter. If such a bias was driving the pattern of male mass loss, we would also expect mass decay to be strong when hunting begins on 10 September until around the start of October, when rutting intensity increases. However, for this hunting period there is no or very slight mass loss (see Results). Indeed, some age classes increase in body mass before the rut starts, which cannot be explained by biased hunting. Thus, the pattern reported here cannot be explained by hunter selectivity. Also, the patterns of decay are probably not related to decreasing plant quality, as females start to have a negative energy balance much later (indicative of seasonality).

In Soay sheep, males were shown to target their mate-guarding to the optimal insemination window of females (Preston et al. 2003). Our results are consistent with this, showing that the prime-aged males indeed time the maximal use of the capital to the period when mating is at stake (Fig. 1). The later peak mass decline in young males at low density indicates that they target their reproductive effort to the last part of the rut when most of the females have ovulated, when the capital of prime-aged males is becoming depleted. It may also be that prime-aged males are reluctant to invest more into the later parts of autumn due to increased chances of mortality during the subsequent winter (e.g. Toïgo & Gaillard 2003). The best evidence that late investment of young males is a successful strategy comes from the studies on Soay sheep showing increased paternity of younger males later in rut (Preston et al. 2001). While adult males deplete their fat layers, subadults (in the presence of adult males) may even increase their fat layer throughout the rut due to low effort (Komers, Messier & Gates 1994; Mysterud et al. 2003). Yearling females, making up a substantial proportion of the population, are ovulating much later than prime-aged females. The prime aged males therefore seem to target mainly the older and heavier females ovulating early. The possibility that males are selecting for particular females has received little attention in the literature, but has been demonstrated in bison (Bison bison) (Berger 1989) and Soay sheep (Preston et al. 2005). Such issues may be particularly important in harvested populations with a skewed sex ratio.

Many aspects of the life history of ungulates in general is affected by harvesting (Mysterud, Coulson & Stenseth 2002). In our populations, sex ratios have become increasingly female-biased and the male age structure becomes younger with increasing density, due to heavy male-biased harvesting (Langvatn & Loison 1999; Milner et al. 2006). Unfortunately, accurate information on sex ratio development is lacking. However, since 1978 the proportion of males in the adult harvest has been approximately 60% in Norway (Milner et al. 2006), resulting in female-biased populations with < 40% males in the adult segment. The average age of adult males ( 2 years) harvested has declined from 6·5 years in 1965 to 3·1 years in 2003 (population P3; A. Mysterud & R. Langvatn, unpublished information). In populations with a heavy male-biased harvest, young males may be more involved in rut when few prime-aged males are present than in non-harvested populations (Komers et al. 1994; Mysterud et al. 2003). Indeed, we found that even young red deer males decline in body mass during rut (Yoccoz et al. 2002; this study), but much less than prime-aged males. The maximum daily mass loss for Norwegian red deer males during rut was 0·1, 0·3, 0·6, 0·7, 0·9 and 1·0% for, respectively, yearlings, 2-year-olds, 3-year-olds, 4-year-olds, 5–7-year-olds and more than 7-year-olds. Note, however, that the relationship between effort and reproductive success in males is complicated by differences in individual quality (McElligott et al. 2003; Pelletier 2005; Pelletier et al. 2006).

In addition to increasingly female-biased sex ratios and younger male age structure with increasing population density, there is another independent process that can also decrease the level of male competition. The ovulation period is more synchronized at high density than at low density (from 10 to 80% in 13 days at high vs. 21 days at low density; Langvatn et al. 2004). Thus, depending on the male's ability to gather and defend females, and hence on female spatial distribution (Jarman 1974; Emlen & Oring 1977), a high number of receptive females at the same time may decrease the chances of dominant males to monopolize all females. In our Norwegian populations females live in small scattered groups, averaging only 1·5 females per male in mixed groups during rut (Bonenfant et al. 2004), and monopolizing many synchronized females at the same time is unlikely for a single male. Both these patterns can thus relieve the intensity of sexual selection processes with increasing density (Wade, Shuster & Demuth 2003; Wade & Shuster 2004). Consistent with such a scenario, male age groups were indeed more synchronized in their peak decay at high density, suggesting that males of different ages were more able to mate successfully during peak rut at high density (see also Coltman et al. 1999 on Soay sheep). This provides evidence for the suggestion that male rutting phenology in capital breeders is best interpreted as a compromise between hitting peak female ovulation and the level of sexual selection forces that may change with population density. Such a lowering of sexual selection forces may, in turn, lead to a higher effective population size, if a higher proportion of males gain successful mating (Hard, Mills & Peek 2007).

Acknowledgements

  1. Top of page
  2. Summary
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Supporting Information

These analyses were made possible by the YFF grant from the Research Council of Norway to A.M., from which C.B. and L.E.L. also received funding. The red deer monitoring programme is funded by the Directorate for Nature Management. We are grateful to Tim Coulson, Marco Festa-Bianchet and Fanie Pelletier for constructive comments on a previous draft.

References

  1. Top of page
  2. Summary
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Supporting Information
  • Abrahamsen, J., Jacobsen, N.K., Kalliola, R., Dahl, E., Wilborg, L. & Påhlsson, L. (1977) Nature geographic regions of the Nordic countries. Nordiske Utredninger Series B, 34, 1135.
  • Alvarez, F. (1993) Risks of fighting in relation to age and territory holding in fallow deer. Canadian Journal of Zoology, 71, 376383.
  • Berger, J. (1989) Female reproductive potential and its apparent evaluation by male mammals. Journal of Mammalogy, 70, 347358.
  • Bonenfant, C., Loe, L.E., Mysterud, A., Langvatn, R., Stenseth, N.C., Gaillard, J.M. & Klein, F. (2004) Multiple causes of sexual segregation in European red deer: enlightenments from varying breeding phenology at high and low latitude. Proceedings of the Royal Society of London, Series B, 271, 883892.
  • Clutton-Brock, T.H., Albon, S.D., Gibson, R.M. & Guinness, F.E. (1979) The logical stag: adaptive aspects of fighting in red deer (Cervus elaphus L.). Animal Behaviour, 27, 211225.
  • Clutton-Brock, T.H., Albon, S.D. & Guinness, F.E. (1988) Reproductive success in male and female red deer. Reproductive Success (ed. T.H.Clutton-Brock), pp. 325343. University of Chicago Press, Chicago.
  • Clutton-Brock, T.H., Guinness, F.E. & Albon, S.D. (1982) Red Deer. Behaviour and Ecology of Two Sexes. Edinburgh University Press, Edinburgh.
  • Clutton-Brock, T.H. & Parker, G.A. (1992) Potential reproductive rates and the operation of sexual selection. Quarterly Review of Biology, 67, 437456.
  • Coltman, D.W., Festa-Bianchet, M., Jorgenson, J.T. & Strobeck, C. (2002) Age dependent sexual selection in bighorn rams. Proceedings of the Royal Society of London, Series B, 269, 165172.
  • Coltman, D.W., Smith, J.A., Bancroft, D.R., Pilkington, J., MacColl, A.D.C., Clutton-Brock, T.H. & Pemberton, J.M. (1999) Density dependent variation in lifetime breeding success and natural and sexual selection in Soay rams. American Naturalist, 154, 730746.
  • R Development Core Team (2007) r: A Language and Environment for Statistical Computing. R Foundation for Statistical Computing, Vienna, Austria.
  • Emlen, S.T. & Oring, L.W. (1977) Ecology, sexual selection and the evolution of mating systems. Science, 197, 215223.
  • Festa-Bianchet, M. (1988) Birthdate and lamb survival in bighorn lambs (Ovis canadensis). Journal of Zoology, 214, 653661.
  • Festa-Bianchet, M., Gaillard, J. M. & Jorgenson, J.T. (1998) Mass and density dependent reproductive success and reproductive costs in a capital breeder. American Naturalist, 152, 367379.
  • Forsyth, D.M., Duncan, R.P., Tustin, K.G. & Gaillard, J.M. (2005) A substantial energetic cost to male reproduction in a sexually dimorphic ungulate. Ecology, 86, 21542163.
  • Geist, V. (1974) On fighting strategies in animal combat. Nature, 150, 354.
  • Hamlin, K.L., Pac, D.F., Sime, C.A., DeSimone, R.M. & Dusek, G.L. (2000) Evaluating the accuracy of ages obtained by two methods for Montana ungulates. Journal of Wildlife Management, 64, 441449.
  • Hard, J.J., Mills, L.S. & Peek, J.M. (2007) Genetic implications of reduced survival of male red deer Cervus elaphus under harvest. Wildlife Biology, 12, 427439.
  • Harrison, R.J. & Weir, B.J. (1977) Structure of the mammalian ovary. The Ovary (eds L.Zuckerman & B.J.Weirs), pp. 113217. Academic Press, New York.
  • Hastie, T. & Tibshirani, R. (1990) Generalized Additive Models. Chapman & Hall, London.
  • Hogg, J.T. (1984) Mating in bighorn sheep: multiple creative male strategies. Science, 225, 526529.
  • Hogg, J.T. & Forbes, S.H. (1997) Mating in bighorn sheep: frequent male reproduction via a high risk ‘unconventional’ tactic. Behavioral Ecology and Sociobiology, 41, 3348.
  • Holand, Ø., Mysterud, A., Røed, K.H., Coulson, T., Gjøstein, H., Weladji, R.B. & Nieminen, M. (2006) Adaptive adjustment of offspring sex ratio and maternal reproductive effort in an iteroparous mammal. Proceedings of the Royal Society of London, Series B, 273, 293299.
  • Hurrell, J.W. (1995) Decadal trends in the North Atlantic Oscillation: regional temperatures and precipitation. Science, 269, 676679.
  • Hurrell, J.W., Kushnir, Y., Ottersen, G. & Visbeck, M. (2003) The North Atlantic Oscillation. Climatic Significance and Environmental Impact. American Geophysical Union, Washington, DC.
  • Jarman, P.J. (1974) The social organisation of antelope in relation to their ecology. Behaviour, 48, 215266.
  • Jönsson, K.I. (1997) Capital and income breeding as alternative tactics of resource use in reproduction. Oikos, 78, 5766.
  • Kojola, I. (1991) Influence of age on the reproductive effort of male reindeer. Journal of Mammalogy, 72, 208210.
  • Komers, P.E., Messier, F. & Gates, C.C. (1994) Plasticity of reproductive behaviour in wood bison bulls: when subadults are given a chance. Ethology, Ecology and Evolution, 6, 313330.
  • Lambin, X. & Yoccoz, N.G. (2001) Adaptive precocial reproduction in voles: reproductive costs and multivoline life history strategies in seasonal environments. Journal of Animal Ecology, 70, 191200.
  • Langvatn, R. (1977) Criteria of Physical Condition, Growth and Development in Cervidae – Suitable for Routine Studies. Nordic Council for Wildlife Research, Stockholm.
  • Langvatn, R. (1992) Analysis of ovaries in studies of reproduction in red deer (Cervus elaphus L.): application and limitations. Rangifer, 12, 6791.
  • Langvatn, R. & Loison, A. (1999) Consequences of harvesting on age structure, sex ratio and population dynamics of red deer Cervus elaphus in central Norway. Wildlife Biology, 5, 213223.
  • Langvatn, R., Mysterud, A., Stenseth, N.C. & Yoccoz, N.G. (2004) Timing and synchrony of ovulation in red deer constrained by short northern summers. American Naturalist, 163, 763772.
  • Loe, L.E., Bonenfant, C., Mysterud, A., Gaillard, J.M., Langvatn, R., Stenseth, N.C., Klein, F., Calenge, C., Ergon, T. & Pettorelli, N. (2005) Climate predictability and breeding phenology in red deer: timing and synchrony of rutting and calving in Norway and France. Journal of Animal Ecology, 74, 579588.
  • Loe, L.E., Meisingset, E.L., Mysterud, A., Langvatn, R. & Stenseth, N.C. (2004) Phenotypic and environmental correlates of tooth eruption in red deer (Cervus elaphus). Journal of Zoology, 262, 8389.
  • Loison, A., Langvatn, R. & Solberg, E.J. (1999) Body mass and winter mortality in red deer calves: disentangling sex and climate effects. Ecography, 22, 2030.
  • Maher, C.R. & Byers, J.A. (1987) Age related changes in reproductive effort of male bison. Behavioral Ecology and Sociobiology, 21, 9196.
  • Martínez, M., Rodríquez, V., Jones, O.R., Coulson, T. & San Miguel, A. (2005) Different hunting strategies select for different weights in red deer. Biology Letters, 1, 353356.
  • McComb, K. (1987) Roaring by red deer stags advances the date of oestrus in hinds. Nature, 330, 648649.
  • McElligott, A.G., Naulty, F., Clark, W.V. & Hayden, T.J. (2003) The somatic cost of reproduction: what determines reproductive effort in prime aged fallow bucks? Evolutionary Ecology Research, 5, 112.
  • Milner, J.M., Bonenfant, C., Mysterud, A., Gaillard, J.M., Csányi, S. & Stenseth, N.C. (2006) Temporal and spatial development of red deer harvesting in Europe – biological and cultural factors. Journal of Applied Ecology, 43, 721734.
  • Miquelle, D.G. (1990) Why don't bull moose eat during the rut? Behavioral Ecology and Sociobiology, 27, 145151.
  • Mysterud, A. (2004) Temporal variation in the number of car killed red deer Cervus elaphus in Norway. Wildlife Biology, 10, 203211.
  • Mysterud, A., Yoccoz, N.G., Stenseth, N.C. & Langvatn, R. (2001c) The effects of age, sex and density on body weight of Norwegian red deer: evidence of density dependent senescence. Proceedings of the Royal Society of London, Series B, 268, 911919.
  • Mysterud, A., Coulson, T. & Stenseth, N.C. (2002) The role of males in the population dynamics of ungulates. Journal of Animal Ecology, 71, 907915.
  • Mysterud, A., Holand, Ø., Røed, K.H., Gjøstein, H., Kumpula, J.M. & Nieminen, M. (2003) Effects of age, density and sex ratio on reproductive effort in male reindeer (Rangifer tarandus). Journal of Zoology, 261, 341344.
  • Mysterud, A., Langvatn, R. & Stenseth, N.C. (2004) Patterns of reproductive effort in male ungulates. Journal of Zoology, 264, 209215.
  • Mysterud, A., Langvatn, R., Yoccoz, N.G. & Stenseth, N.C. (2001a) Plant phenology, migration and geographic variation in body weight of a large herbivore: the effect of a variable topography. Journal of Animal Ecology, 70, 915923.
  • Mysterud, A., Langvatn, R., Yoccoz, N.G. & Stenseth, N.C. (2002) Large scale habitat variability, delayed density effects and red deer populations in Norway. Journal of Animal Ecology, 71, 569580.
  • Mysterud, A., Meisingset, E.L., Veiberg, V., Langvatn, R., Solberg, E.J., Loe, L.E. & Stenseth, N.C. (2007) Monitoring population size of red deer: an evaluation of two types of census data from Norway. Wildlife Biology, 13, 285298.
  • Mysterud, A., Solberg, E.J. & Yoccoz, N.G. (2005) Ageing and reproductive effort in male moose under variable levels of intra sexual competition. Journal of Animal Ecology, 74, 742754.
  • Mysterud, A., Stenseth, N.C., Yoccoz, N.G., Langvatn, R. & Steinheim, G. (2001b) Nonlinear effects of large scale climatic variability on wild and domestic herbivores. Nature, 410, 10961099.
  • Mysterud, A., Tryjanowski, P. & Panek, M. (2006) Selectivity of harvesting differs between local and foreign roe deer hunters – trophy stalkers have the first shot at the right place. Biology Letters, 2, 632635.
  • Pelletier, F. (2005) Foraging time of rutting bighorn rams varies with individual behavior, not mating tactic. Behavioral Ecology, 16, 280285.
  • Pelletier, F., Hogg, J.T. & Festa-Bianchet, M. (2006) Male mating effort in a polygynous ungulate. Behavioral Ecology and Sociobiology, 60, 645654.
  • Pemberton, J.M., Albon, S., Guinness, F.E., Clutton-Brock, T.H. & Dover, G.A. (1992) Behavioral estimates of male mating success tested by DNA fingerprinting in a polygynous mammal. Behavioral Ecology, 3, 6675.
  • Pettorelli, N., Mysterud, A., Yoccoz, N.G., Langvatn, R. & Stenseth, N.C. (2005) Importance of climatological downscaling and plant phenology for red deer in heterogeneous landscapes. Proceedings of the Royal Society of London, Series B, 272, 23572364.
  • Preston, B.T., Stevenson, I.R., Pemberton, J.M., Coltman, D.W. & Wilson, K. (2005) Male mate choice influences female promiscuity in Soay sheep. Proceedings of the Royal Society of London, Series B, 272, 365373.
  • Preston, B.T., Stevenson, I.R. & Wilson, K. (2003) Soay rams target reproductive activity towards promiscuous females’ optimal insemination period. Proceedings of the Royal Society of London, Series B, 270, 20732078.
  • Preston, B.T., Stevenson, I.R., Pemberton, J.M. & Wilson, K. (2001) Dominant rams lose out by sperm depletion. A waning success in siring counters a ram's high score in competition for ewes. Nature, 409, 681682.
  • Solberg, E.J., Loison, A., Sæther, B.E. & Strand, O. (2000) Age specific harvest mortality in a Norwegian moose Alces alces population. Wildlife Biology, 6, 4152.
  • Statistics Norway (2004) Official Hunting Statistics of Norway. Statistics Norway, Oslo and Kongsvinger.
  • Stutchbury, B.J. & Morton, E.S. (1995) The effect of breeding synchrony on extra pair mating systems in songbirds. Behaviour, 132, 675690.
  • Toïgo, C. & Gaillard, J.M. (2003) Causes of sex biased adult survival in ungulates: sexual size dimorphism, mating tactic or environment harshness? Oikos, 101, 376684.
  • Ulm, K. (1989) On the estimation of threshold values. Biometrics, 45, 13241326.
  • Wade, M.J. & Shuster, S.M. (2004) Sexual selection: harem size and the variance in male reproductive success. American Naturalist, 164, E83.
  • Wade, M.J., Shuster, S.M. & Demuth, J.P. (2003) Sexual selection favors female biased sex ratios: the balance between the opposing forces of sex ratio selection and sexual selection. American Naturalist, 162, 403414.
  • Wallin, K., Cederlund, G. & Pehrson, Å. (1996) Predicting body mass from chest circumference in moose Alces alces. Wildlife Biology, 2, 5358.
  • Willisch, C.S. & Ingold, P. (2007) Feeding or resting? The strategy of rutting male alpine chamois. Ethology, 113, 97104.
  • Wood, S. (2006) Generalized Additive Models: an Introduction with r. Chapman & Hall, Boca Raton.
  • Yoccoz, N.G., Mysterud, A., Langvatn, R. & Stenseth, N.C. (2002) Age and density dependent reproductive effort in male red deer. Proceedings of the Royal Society of London, Series B, 269, 15231529.

Supporting Information

  1. Top of page
  2. Summary
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Supporting Information

Appendix S1. Temporal vs. spatial density dependence

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