| Literature DB >> 26601284 |
Nina Vasilieva1, Andrey Tchabovsky1.
Abstract
Sexual conflict theory suggests that female breeding success is strongly influenced by individual life history and environmental conditions and is much less affected by mate availability. Female mating failure due to a shortage of males remains poorly studied and understood. We present data on the effects of male availability on female breeding success in a wild colony of yellow ground squirrels (Spermophilus fulvus). A female's probability of breeding increased with the local density of males and was higher with higher male-biased operational sex ratio (OSR) but was independent of local female density, female age, and body condition, which are factors commonly assumed to influence female reproduction. The positive effect of male availability (as measured by OSR) on female breeding success was consistent across the years, and we conclude that male limitation contributes to female mating failure. This pattern, which is not commonly recorded in species with conventional sex roles, can be explained by a combination of sociodemographic and life history traits (sex differences in age of maturation, female-skewed adult sex ratio and seasonally varying OSR, solitary living at low population density, and low mobility of females combined with mate-searching tactics of males) that are not confined to S. fulvus. Our findings indicate that the role of female mating failure (due to a shortage of males) in shaping mammalian life history may be underestimated.Entities:
Keywords: female reproduction; ground squirrels; male availability; operational sex ratio; reproductive failure
Year: 2015 PMID: 26601284 PMCID: PMC4646798 DOI: 10.1126/sciadv.1500401
Source DB: PubMed Journal: Sci Adv ISSN: 2375-2548 Impact factor: 14.136
Fig. 1Seasonal dynamics of emergence and adult sex ratio in a wild colony of yellow sousliks.
Cumulative portions of emerged squirrels by sex-age categories are shown (N = 244, nmales = 54, nadult females = 120, nyearling females = 70; a pooled data sample for 2004–2007).
Fig. 2Seasonal dynamics of OSR and female breeding success.
Breeding success is measured as a portion of subsequent breeders from all females emerged at 5-day intervals. Numbers in boxes are sample sizes of females with determined breeding status. OSR is presented as mean ± SE at 5-day intervals (a pooled data sample for 2004–2007). The mating season is subdivided into early season (<5 days after the beginning), middle season (5 to 20 days), and late season (>20 days).
Effects of local male density, local female density, and standardized OSR at spring emergence on female reproduction in GLMM.
Female identity was fitted as a random effect in all models. B and SE correspond to model-averaged parameter estimates and SEs in GLMM, whereas χ2 corresponds to likelihood ratio test. All interactions between predictors were insignificant (P > 0.1).
| Local male density (PC1) | ||
| Local female density (PC2) | ||
| OSR (female/male) | ||
| Female age | ||
AICc values for candidate models describing the effects of local male density (Males), local female density (Females), OSR, and female age (Age) on female breeding status in yellow ground squirrels.
Female identity was fitted as a random effect in all models (n = 98). k is the number of parameters estimated by the model, ΔAICc is the difference between the AICc score of the given model and AICc score of the best model (the lowest AICc score was 108.0), and AICc weight reflects relative support for each model. Models with ΔAICc > 2.0 are in boldface.
| OSR + Males + Females | 5 | 2.2 | 0.14 |
| OSR + Males + Females + Age | 6 | 3.1 | 0.09 |
| OSR + Age | 4 | 7.3 | 0.01 |
| Males | 3 | 8.0 | 0.01 |
| OSR | 3 | 8.4 | 0.01 |
| Males + Age | 4 | 9.3 | 0.00 |
| Males + Females | 4 | 9.4 | 0.00 |
| OSR + Females + Age | 5 | 9.4 | 0.00 |
| OSR + Females | 4 | 10.6 | 0.00 |
| Males + Females + Age | 5 | 10.9 | 0.00 |
| Age | 3 | 15.1 | 0.00 |
| Intercept | 2 | 15.2 | 0.00 |
| Females | 3 | 16.8 | 0.00 |
| Females + Age | 4 | 17.0 | 0.00 |
OSR and parameters of male and female distribution at female vernal emergence for subsequent breeders and nonbreeders.
Data are presented as mean ± SD [range] (n) (see statistics in Table 1).
| Mean distance to the five | 95 ± 54 [26–236] (18) | 106 ± 57 [42–251] (38) | 152 ± 60 [29–230] (12) | 105 ± 34 [59–251] (16) |
| Number of male* burrows within 100 m | 3.2 ± 2.3 [0–6] (18) | 3.1 ± 1.7 [0–6] (38) | 1.7 ± 1.6 [0–6] (12) | 2.4 ± 1.4 [1–5] (16) |
| Mean distance to the five nearest | 50 ± 29 [26–128] (18) | 66 ± 61 [18–352] (38) | 50 ± 26 [23–95] (12) | 59 ± 30 [18–109] (16) |
| Number of female† burrows within 70 m | 3.4 ± 3.1 [0–9] (18) | 3.7 ± 3.1 [0–12] (38) | 2.5 ± 2.2 [0–8] (12) | 2.9 ± 2.3 [0–9] (16) |
| OSR (female/male) | 0.6 ± 0.3 [0.2–1.1] (27) | 0.7 ± 0.4 [0.08–1.3] (47) | 0.9 ± 0.3 [0.6–1.2] (12) | 1.0 ± 0.3 [0.2–1.3] (19) |
*Only ≥2-year-old males that emerged no later than the fifth day after the date of emergence of the focal female.
†Only females that emerged within ±5 days from the date of emergence of the focal female.
Fig. 3Effects of OSR at emergence on female breeding success across the years.
The effects were highly significant in GLMM (P = 0.0008). The sample sizes are 25, 33, 37, and 31 females for 2004–2007, respectively. Error bars represent mean ± 95% confidence interval.