Behavioral Ecology Vol. 14 No. 2: 268-273
© 2003 International Society for Behavioral Ecology
Male mating behavior and ejaculate expenditure under sperm competition risk in the eastern mosquitofish
Department of Biology, University of Padova, Via U. Bassi 58/B, Padova I-35131, Italy
Address correspondence to I. Pilastro. E-mail: andrea.pilastro{at}unipd.it.
Received 18 March 2002; revised 18 July 2002; accepted 20 July 2002.
| ABSTRACT |
|---|
|
|
|---|
Theory predicts that males should tailor the size of their ejaculates according to temporal changes in the risk of sperm competition. Specifically, males are predicted to allocate more sperm to each mating event with increasing risk (i.e., the probability that the sperm from two males will compete for fertilization). We tested this hypothesis by using the eastern mosquitofish, a freshwater species of fish exhibiting a coercive mating system and internal fertilization. We manipulated the perception of sperm competition risk by adjusting the sex ratio under which males were maintained over 8 days. Males were housed either with three females and one male (simulating high sperm competition risk) or with four females (low risk). After the treatment, we presented each test male individually to an unfamiliar male-deprived female for 30 minutes and observed his mating behavior. We then artificially stripped the test males of sperm and recovered the ejaculates from the females. Our results revealed that males in the high-risk group performed higher levels of mating activity and sperm expenditure (i.e., used up more of their sperm reserves) than did low-risk males. A control experiment, in which test males were treated but did not participate in the mating trials, revealed no significant difference in the number of sperm stripped from high- and low-risk males, indicating that sperm production was not affected by the treatment. We did not detect a difference in the number of sperm retrieved from females among the groups, raising the possibility that some sperm are lost during mating activity, either through ejaculation with incomplete or interrupted penetration, or via female ejection.
Key words: coercive matings, guppy, Poeciliidae, sperm competition theory, sperm store.
| INTRODUCTION |
|---|
|
|
|---|
Sexual selection will favor any adaptation in males that increases their success in sperm competition, defined as the contest between the sperm from two or more males for the fertilization of a set of eggs (Parker, 1970
In fishes, in which the majority of sperm competition studies have focused on externally fertilizing group-spawning species (for review, see Petersen and Warner, 1998
), interspecific patterns of male gametic investment have been shown to co-vary with sperm competition intensity in accordance with theoretical predictions (Stockley et al., 1997
). Studies that have focused on within-species patterns of sperm production have tended to examine groups in which males exhibit alternative mating tactics (Gage et al., 1995
; Gross, 1982
; Petersen, 1990
; Pilastro and Bisazza, 1999
; Robertson and Warner, 1978
; Warner and Robertson, 1978
) rather than on those in which individual males face varying levels of sperm competition among a series of spawns (Fuller, 1998
; Petersen and Warner, 1998
). Furthermore, no studies have examined the ejaculation strategies of species exhibiting internal fertilization, even though they are ideally suited for such studies. Unlike in external fertilizers, in which the assessment of sperm competition risk can be problematic owing to the difficulty in measuring the number of males actually participating in a spawning event, it is relatively easy to both manipulate and assess the level of sperm competition in internal fertilizers (see Petersen and Warner, 1998
).
Previous studies on sperm competition in internally fertilizing fish have focused almost exclusively on one family, the Poeciliidae (see Constantz, 1984
; Evans and Magurran, 2001
; Hildemann and Wagner, 1954
; Pilastro and Bisazza, 1999
; Zane et al., 1999
). Poeciliids are a group of live-bearing fish, native to the New World but introduced elsewhere as mosquito control agents and ornamental fish. Among these, the eastern mosquitofish Gambusia holbrooki was introduced into Italian fresh and brackish waters at the beginning of last century (Dulzetto, 1928
). As in other poeciliids, fertilization in eastern mosquitofish is internal, and during copulation, males transfer sperm in bundles (spermatozeugmata) by inserting their modified anal fin, the gonopodium, into the female's genital pore (Constantz, 1989
). Shortly after insemination, the sperm bundles break apart in the gonoduct, and spermatozoa not immediately used for fertilization can be stored for several months (Dulzetto, 1928
). Females are ovoviviparous, retaining yolked embryos without nourishing them (Constantz, 1989
). Unlike some poeciliids, in which individual males display alternative mating tactics (for review, see Meffe and Snelson, 1989
)
, male eastern mosquitofish appear to exhibit no courtship and achieve inseminations through gonopodial thrusts (Bisazza, 1993
; McPeek, 1992
). High levels of multiple paternity within the broods of the eastern mosquitofish (Zane et al., 1999
), coupled with the females' ability to store sperm (Constantz, 1984
, 1989
), suggests that sperm competition is intense in the species.
In the present study, we investigate the effect of varying sperm competition risk on the mating behavior and sperm expenditure of male G. holbrooki. As Parker (1998)
notes, engaging in repeated copulations toward individual females is a means by which males can adjust sperm allocation in response to changes in the risk of sperm competition. This strategy is likely to be especially important when males are limited in their ability to tailor the size of individual ejaculates during a single copulation (see Birkhead and Møller, 1992
). Such a constraint is likely to apply to male G. holbrooki, in which gonopodial thrusts, each lasting a fraction of a second, are performed repeatedly towards individual females. Consequently, there is likely to be minimal scope for adjusting ejaculate size during individual gonopodial thrusts in this species. Accordingly, we anticipated a general increase in the frequency of coercive mating attempts by males, resulting in increased sperm allocation and higher levels of sperm expenditure under elevated sperm competition risk. Incidences in which spermatozeugmata are released into the water during male mating attempts have been observed in mosquitofish (Evans JP, Pierotti M, Pilastro A, unpublished observations). We therefore considered as a measure of sperm expenditure (allocation) both the number of sperm inseminated and the sperm reserves left after the experiment.
| METHODS |
|---|
|
|
|---|
The study population and its maintenance
Eastern mosquitofish were collected early in the breeding season (which lasts from May until September) from Valle Averto, a system of brackish water ponds and ditches in the Venetian lagoon basin (northern Italy). Early in the season, the sex ratio of natural populations is typically biased toward females owing to differential malefemale survival over winter (Zulian et al., 1995
Sperm competition risk treatment
Sexually mature males, recognizable by their fully developed intromittent organ (the gonopodium), were chosen randomly from several stock tanks and placed for 8 days in 90-l treatment tanks containing either (1) four females (stimulus fish to simulate low-sperm competition risk) or (2) three females and a male (simulating high risk). The two sex ratios fall within the range naturally encountered by males in the wild, and are known to change over similar time scales to the one chosen for our study (Zulian et al., 1995
). Following the 8-day treatment period, focal males were moved into the experimental tanks for the mating trials (see Mating Trials below), and the stimulus fish were returned to stock aquaria and replaced by others for the next trials. All fish (focal and stimulus) were assigned randomly to each experimental group, and tanks were randomized with respect to treatment. Treatment tanks contained natural gravel, air filters, and green plastic comblike barriers designed to create a heterogeneous environment for the fish. Sample sizes for the experiment were n = 31 (low risk) and n = 25 (high risk).
Mating trials
Focal males were individually placed into one of four experimental tanks (35 x 45 x40 cm, filled to a depth of 30 cm) and left to acclimatize overnight. Attached to each of these tanks was a second smaller tank (20 x 15 x 15 cm) in which we placed stimulus fish designed to maintain each focal male's perception of sperm competition risk during the acclimation period. In each experimental tank containing a "high-risk" male, the small tank contained three females and a male (unfamiliar to the test male). Likewise, in the low-risk tanks, we placed four females in the small enclosure. We ensured that the test males had visual but not olfactory access to the stimulus fish. Treatments were randomized among the four experimental tanks to avoid possible bias.
On the following morning, the small tanks containing the stimulus fish were carefully removed from the experimental aquarium. We then placed a male-deprived female (who was consequently naïve of the experimental treatment) into the tank with the male and began our behavioral observations as soon as the male performed his first mating attempt. These were characterized by the male approaching the female with his gonopodium swung forward (more than 90° angle) and his snout drawing level or beyond the tip of the female's caudal fin (Pilastro et al., 1997
). We also recorded the number of genital contacts between males and females, which were highly conspicuous owing to the female's "jolting" response when the male's gonopodium made physical contact with her genital region. Mating trials lasted 30 min (from the first mating attempt), and to estimate male mating behavior, we considered the number of mating attempts and genital contacts performed during the initial 20 min of each trial. All behavioral observations were performed blind of experimental group (i.e., the observer was not aware of the test male's treatment status), and each trial was video-recorded to aid our subsequent analysis of male behavior. Mating trials took place between 0900 and 1400 h.
Control experiment
The time required for full sperm replenishment has not been investigated in eastern mosquitofish, but observations in guppies (Poecilia reticulata) suggest that males can restore their sperm reserves in 1 day (Kuckuck and Greven, 1997
). Nonetheless, in a separate experiment, we controlled for the possibility that test males in the 2 experimental groups entered the mating trials with different-sized sperm reserves, for example, as a result of differential sperm production or mating activity among the two treatment groups. We performed a series of identical trials to those described above in which control males were treated for 8 days (high-risk, n = 14; low-risk, n = 13) but did not participate in the mating trials. Instead, these males were allowed to rest overnight (as in the experimental groups) and were then artificially stripped of sperm (see below). Sperm counts were then compared among males from both groups to control for the potentially confounding effect that males entered the mating trials with different sized sperm reserves.
Sperm counts
Within 10 min of the behavioral trials, test males and females were isolated, anaesthetized with MS222, and placed on a Petri dish under a dissection microscope. For each male, standard length (SL) was measured to the nearest 1 mm. To collect sperm from males, the gonopodium was swung forward to induce the formation of a temporary groove through which sperm bundles could pass; gentle pressure applied to the side of the abdomen, at the base of the gonopodium, induced sperm release (Constantz, 1984
; Peden, 1972
). After repeating this action to remove all sperm bundles, the stripped ejaculate was recovered under low magnification by using a glass micropipette and diluted in 100 µl of physiological solution (0.9% NaCl).
To collect ejaculates from the females, approximately 10 µl of physiological solution was taken from a microtube containing 50 µl of the solution and injected into the female's gonoduct by using a glass micropipette (Pilastro et al., 1997
). Samples were retrieved from the female and returned to the microtube. We repeated this process three times to ensure that we collected all recoverable sperm from the females. All samples (male and female) were subsequently drawn up and expelled from the pipette to aid the breakdown of bundles and to produce an even dispersal of sperm cells. The number of sperm per stripped and natural ejaculate was estimated by using a Bürker counting-chamber under x400 magnification. After checking that sperm cells were evenly distributed across the chamber, sperm number was determined by multiplying the mean from five sperm counts by the sample's dilution factor and initial volume (see Matthews et al., 1997
). As in the mating trials, sperm counts were performed blind of experimental group in order to avoid possible observer bias. We confirmed that the SL of males, females, and control males did not significantly differ between the treatment groups (test males: t53 = 0.22, p =.83; test females: t53 =.41, p =.69; male SL/female SL: t53 = 0.21, p =.84; control males: t53 = 1.13, p =.27). After the extraction of sperm, males and females were revived in conditioned fresh water (Stress Coat, Aquarium Pharmaceuticals Inc., Chalfont, Pennsylvania, USA) and returned to stock aquaria, where they played no further part in the experiment.
Analysis
Statistical analyses were performed by using SPSS 10.1 (Noru
is, 1993
). When data were not normally distributed, we used either log transformation or nonparametric tests. In the latter case, exact probability is given. Because male body size is positively correlated with the number of sperm stripped and negatively correlated with the number of male mating attempts (Bisazza and Marin, 1995
; Pilastro et al., 1997
), we controlled for male size by using an ANCOVA in which treatment was the factor; male SL, the covariate; and male mating attempts or sperm stripped, the dependent variables. In one case (sperm stripped), the variances in the two groups were not homogeneous, even after log transformation. We therefore compared the residuals of the regression of sperm stripped on male length by using a Student's t test for nonhomogeneous variances, and reduced the degrees of freedom by one to account for having used residuals (Noru
is, 1993
). If not otherwise stated, mean ± SE is given. All probabilities are two-tailed. We failed to measure SL of one male and one female and to strip sperm from one male from the low-risk group. Sample sizes can therefore differ between analyses.
| RESULTS |
|---|
|
|
|---|
Males assigned to the high-risk group performed significantly more mating attempts than those in the low-risk treatment (t54 = 2.15, p =.036; Figure 1). To remove the effect of male body size, which was negatively correlated with mating frequency (r = .28, n = 55, p =.04), we performed an ANCOVA with male SL as the covariate. This analysis confirmed that high-risk males performed more mating attempts than did their low-risk counterparts during the 20-min observation period (model: F2,52 = 4.64, p =.014; male SL: F = 4.98, p =.03; treatment: F = 4.58, p =.037). The mean number of genital contacts was slightly higher in the high-risk group, but the difference was not significant (high-risk males: mean = 3.56 ± 0.42, n = 25; low-risk males: mean = 3.29 ± 0.36, n = 31; t54 =.49, p =.63).
|
Our analysis revealed that the number of mating attempts was positively correlated with the number of sperm inseminated among males from both treatments (Spearman rank correlation: rs =.40, n = 56, p =.002). However, we found no significant difference in the number of sperm retrieved from females among the two treatment groups (high-risk treatment: mean = 0.03 x 106 ± 0.12, n = 25; low-risk treatment: mean = 0.03 x 106 ± 0.19, n = 31; U = 364, p =.61, Mann-Whitney U test). In most cases, we did not retrieve sperm from the female (high-risk group = 18/25; low-risk = 24/31); the frequency of females without sperm did not differ between groups (Fisher's exact test: p =.76). When we further categorized males within each treatment group according to whether they successfully inseminated the female (i.e., based on whether sperm were retrieved from the female), we found that successful males (n = 14) performed significantly more mating attempts than did those who failed to inseminate the female (n = 42, t54 = 3.03, p =.004; Figure 2). In addition, successful males obtained more genital contacts than did unsuccessful ones (n1 = 14, n2 = 42, U = 172.5, p =.016).
|
Our analysis revealed that high-risk males stripped fewer sperm after the mating trials than their low-risk counterparts (analysis by using residuals of the regression between body size and the number of stripped sperm: t51 = 2.26, p =.035; Figure 3). This finding was supported by the results from the control experiment, which confirmed that high- and low-risk males did not enter the mating trials with different-sized sperm reserves (mean sperm counts: high-risk males = 1.07 x 106 ± 0.36, n = 14; low-risk males = 1.07 x 106 ± 0.87, n = 13; t25 = 0.91, p =.37, after log transformation). There was no significant difference in the number of sperm stripped between the two groups in the control experiment even after controlling for male size (ANCOVA, model: F2,26 = 4.10, p =.029; male SL: F = 7.17, p =.013; treatment: F = 0.014, p =.91). Some males did not strip any sperm in the control experiment (Fisher's exact test: high-risk = 5/14; low-risk = 3/13; p =.68), and when these males were removed from the analysis, high-risk males stripped significantly more sperm than did low-risk ones (t18 = 3.17, p =.005). This further supports our conclusion that in the experimental treatments, sperm expenditure during the mating trials by high-risk males was greater than by the low-risk group.
|
| DISCUSSION |
|---|
|
|
|---|
Our results indicate that male eastern mosquitofish strategically allocate both mating effort and sperm output in response to varying sperm competition risk (as simulated by variation in the sex ratio). Males in the high-risk group performed significantly more mating attempts than did those assigned to the competition-free group. Furthermore, our finding that the number of sperm per stripped ejaculate was significantly lower in high-risk males after the mating trials suggests that they respond to the elevated risk of sperm competition by increasing their expenditure on sperm. This conclusion was supported by the results from the control experiment, which confirmed that sperm production was not (significantly) affected by the treatment. A recent study has confirmed that sperm production is unaffected by sperm competition risk even when the treatment period is extended to 16 days (Evans JP, Pierotti M, Pilastro A, unpublished observations).
To our knowledge, this is the first evidence that individual males vary their sperm expenditure according to sperm competition risk in an internally fertilizing species of fish. In other studies, empirical support for strategic ejaculation comes mainly from insects (see Simmons and Siva-Jothy, 1998
, and references therein). For example, in the Indian meal moth (Plodia interpunctella), males strategically allocate sperm in response to the presence and size of rival sperm bundles (spermatophores) in the female reproductive tract (Cook and Gage, 1995
). Two recent studies confirm that male birds also tailor the size of their ejaculates in response to their perception of sperm competition risk (Hunter et al., 2000
; Nicholls et al., 2001
).
Importantly, our analysis revealed that higher mating effort by males increases the likelihood of successful insemination. When we categorized females according to whether sperm were retrieved from their gonoducts, we found that in "successful" trials, males performed more mating attempts than did unsuccessful ones, irrespective of treatment group, which also affected mating effort (see Figure 2). This strongly suggests that male mating success (in terms of sperm transfer) is influenced by the number of attempts made, rather than on the number of sperm allocated per mating attempt (see discussion by Parker, 1998
). However, despite the differences in mating effort among the groups (and its subsequent advantage in terms of insemination success), our results indicated that few males succeeded in inseminating the female. This suggests that males waste part of their sperm output during gonopodial thrusts. Indeed, in the mating trials, and during our subsequent observations of video footage taken during the trials, we noted several incidences in which spermatozeugmata were released into the water. Unfortunately, it was not possible to determine whether these sperm bundles were ejected by females or were instead the result of ejaculations with incomplete or interrupted penetration by males. It would be interesting to determine the frequency of contacts that result in sperm loss because it may represent a substantial energetic cost for the male. An intriguing possibility is that sperm transfer is partially under female control, for instance, via the selective rejection (Eberhard and Cordero, 1995
; Pizzari and Birkhead, 2000
) or replacement (see Constantz, 1984
) of spermatozoa after forced copulations. This possibility clearly warrants further investigation.
Other plausible explanations to account for low insemination success uncovered by our study include the possibility that our extraction method was unreliable. However, previous work has confirmed that it is possible to extract sperm from recently mated female mosquitofish by using identical techniques to the ones used here (Giacomello, 1995
; Pilastro et al., 1997
). In addition, it is possible that the 30-min mating trials provided insufficient time for all males to achieve successful insemination. Although extending the duration of the mating trials may have resulted in a higher proportion of females being inseminated (Giacomello, 1995
), the effect of the treatment may have been weakened or diminished if we had chosen considerably longer trial periods. Moreover, the number of recoverable sperm from the gonoduct of female poeciliids is known to decrease over time (Constantz, 1984
), although the precise rate of decline is presently unknown.
According to our results, male eastern mosquitofish tune their mating behavior in response to the sex ratio they have experienced previously rather than by instantaneously assessing the number of competitors at the time of mating. In our experiment, each experimental male was paired with a single female during the mating trials and therefore would have perceived low sperm-competition risk during the mating trials. We chose this design both because of its biological relevance (see below), and because it avoided the confounding influence of differential sex ratio among the experimental treatments at the time of mating. We therefore avoided the possibility that male behavior and ejaculate expenditure was partly influenced by interactions between the female with whom he had mated (who in our study was naïve of the experimental treatment) and a stimulus male (in the case of the high-risk treatment). In addition, our experimental design was biologically realistic because male eastern mosquitofish do not participate in stable schools but instead move from one group of females (usually two to five females) to another (Zulian et al., 1995
). This makes it impossible for them to instantaneously gauge a given female's past and future mating opportunities (see Parker, 1998
, p. 21 for discussion), and means that a male's best strategy is to assess the average level of sperm competition in the population and adjust his mating effort accordingly. Such a strategy is likely to be important in G. holbrooki, in which sex ratios in wild populations are known to vary predictably over the course of the breeding season in northern Italy. Typically, at the start of the season, sex ratios are biased toward females because of differential over-winter mortality among the sexes (Zulian et al., 1995
; for discussion, see Snelson, 1989
). However, population sex ratios in mosquitofish become increasing male biased as the breeding season progresses, presumably because of differential growth rates and predation pressure among the sexes (Snelson, 1989
; Zulian et al., 1995
).
Although we interpret our results here in the context of sperm competition theory, qualitatively similar results would be expected if males place higher reproductive value to each mating attempt when females are relatively scarce in the population (i.e., similar to our high-risk treatment). In this context, males may also allocate greater mating effort when encountering females. Further work, in which males are exposed to varying numbers of females (but in the absence of a competing male), may help to distinguish between these two alternative hypotheses, although density effects on subsequent male mating behavior may confound the interpretation of the results.
In conclusion, we provide empirical support for Parker et al.'s (1997)
risk model of sperm competition by showing that male eastern mosquitofish tailor their mating behavior and ejaculate expenditure according to variation in the sex ratio. Further investigations are warranted in order to determine whether males also adjust their behavior and ejaculate expenditure in response to variation in the intensity of sperm competition (i.e., when more than two ejaculates compete) in accordance with theoretical predictions (Parker et al., 1996
).
| ACKNOWLEDGEMENTS |
|---|
We are extremely grateful to Angelo Bisazza for providing advice on our experimental design and for the loan of the video recording equipment, and to Jenny Kelley for comments on an earlier version of the manuscript. We also thank staff at the Chioggia Marine Biology Station (Department of Biology, University of Padova) and Mariella Rasotto and her research group for making us feel so welcome. This work was supported by a Marie Curie Independent Fellowship to J.P.E. and a MURST Cofin 2000 grant and an institutional research grant from the University of Padova to A.P.
| References |
|---|
|
|
|---|
Birkhead TR, Møller AP, 1992. Sperm competition in birds: evolutionary causes and consequences. London: Academic Press.
Bisazza A, 1993. Male competition, female mate choice and sexual size dimorphism in poeciliid fishes. In: Behavioural ecology of fishes (Huntingford FA, Torricelli P, eds). Chur, Switzerland: Harwood Academic Press; 257286.
Bisazza A, Marin G, 1995. Sexual selection and sexual size dimorphism in the eastern mosquitofish Gambusia holbrooki (Pisces Poeciliidae). Ethol Ecol Evol 7:169-183.
Constantz GD, 1984. Sperm competition in poeciliid fishes. In: Sperm competition and the evolution of animal mating systems (Smith RL, ed). Orlando, Florida: Academic Press; 465485.
Constantz GD, 1989. Reproductive biology of poeciliid fishes. In: Ecology and evolution of livebearing fishes (Poeciliidae) (Meffe GK, Snelson FF, eds). Englewood Cliffs, New Jersey: Prentice Hall; 3350.
Cook PA, Gage MJG, 1995. Effects of risks of sperm competition on the numbers of eupyrene and apyrene sperm ejaculated by male moth Plodia interpunctella (Lepidoptera: Pyralidae). Behav Ecol Sociobiol 36:261-268.[CrossRef][Web of Science]
Cook PA, Wedell N, 1996. Ejaculate dynamics in butterflies: a strategy for maximizing fertilization success? Proc R Soc Lond B 263:1047-1051.
Dewsbury DA, 1982. Ejaculate cost and male choice. Am Nat 119:601-610.[CrossRef][Web of Science]
Dulzetto F, 1928. Osservazioni sulla vita sessuale di Gambusia holbrooki. Atti R Acc Lincei, Rend 8:96-101.
Eberhard WG, Cordero C, 1995. Sexual selection by cryptic female choice on male seminal products: a new bridge between sexual selection and reproductive physiology. Trends Ecol Evol 10:493-496.[CrossRef]
Evans JP, Magurran AE, 2001. Patterns of sperm precedence and predictors of paternity in the Trinidadian guppy. Proc R Soc Lond B 268:719-724.[Medline]
Fuller RC, 1998. Sperm competition affects male behaviour and sperm output in the rainbow darter. Proc R Soc Lond B 265:2365-2371.
Gage MJG, 1991. Risk of sperm competition directly affects ejaculate size in the Mediterranean fruit fly. Anim Behav 42:1036-1037.[CrossRef][Web of Science]
Gage MJG, 1994. Associations between body size, mating pattern, testis size and sperm lengths across butterflies. Proc R Soc Lond B 258:247-254.
Gage MJG, Barnard CJ, 1996. Male crickets increase sperm number in relation to competition and female size. Behav Ecol Sociobiol 38:349-353.[CrossRef][Web of Science]
Gage MJG, Stockley P, Parker GA, 1995. Effects of alternative male mating strategies on characteristics of sperm production in the Atlantic salmon (Salmo salar): Theoretical and empirical investigations. Philos Trans R Soc Lond B Biol Sci 350:391-399.
Giacomello E, 1995. Dimorfismo maschile e successo riproduttivo in Gambusia holbrooki (Pisces, Poeciliidae) (MSc dissertation). Padova, Italy: University of Padova.
Gross MR, 1982. Sneakers, satellites and parentals: polymorphic mating strategies in North American sunfishes. Z Tierpsychol 60:1-26.[Web of Science]
Harcourt AH, Harvey PH, Larson SG, Short RV, 1981. Testis weight, body weight and breeding system in primates. Nature 293:55-57.[CrossRef][Medline]
Hildemann WH, Wagner ED, 1954. Intraspecific sperm competition in Lebistes. Am Nat 88:87-91.[CrossRef][Web of Science]
Hosken DJ, 1997. Sperm competition in bats. Proc R Soc Lond B 264:385-392.[Medline]
Hunter FM, Harcourt R, Wright M, Davis LS, 2000. Strategic allocation of ejaculates by male Adelie penguins. Proc R Soc Lond B 267:1541-1545.[Medline]
Kuckuck, C., Greven, H., 1997. Notes on the mechanically stimulated discharge of spermiozeugmata in the guppy, Poecilia reticulata: A quantitative approach. Z Fischk 4:73-88.
Matthews IM, Evans JP, Magurran AE, 1997. Male display rate reveals ejaculate characteristics in the Trinidadian guppy Poecilia reticulata. Proc R Soc Lond B 264:695-700.
McPeek MA, 1992. Mechanisms of sexual selection operating on body size in the mosquitofish (Gambusia holbrooki). Behav Ecol 3:1-12.
Meffe GK, Snelson FF, 1989. An ecological overview of poeciliid fishes. In: Ecology and evolution of livebearing fishes (Meffe GK, Snelson FF, eds). Englewood Cliffs, New Jersey: Prentice-Hall; 1331.
Møller AP, 1988. Testis size, ejaculate quality and sperm competition in birds. Biol J Linn Soc 33:273-283.[CrossRef]
Møller AP, 1991. Sperm competition, sperm depletion, paternal care, and relative testis size in birds. Am Nat 137:882-906.[CrossRef][Web of Science]
Nakatsuru K, Kramer DL, 1982. Is sperm cheap? Limited fertility and female choice in the lemon tetra (Pisces, Characidae). Science 216:753-755.
Nicholls EH, Burke T, Birkhead TR, 2001. Ejaculate allocation by male sand martins, Riparia riparia. Proc R Soc Lond B 268:1265-1270.[Medline]
Noru
is MJ, 1993. SPSS for windows based system: User's guide, 6th ed. Chicago: SPSS.
Olsson M, Madson T, Shine R, 1997. Is sperm really so cheap? Costs of reproduction in male adders, Vipera berus. Proc R Soc Lond B 264:455-459.
Parker GA, 1970. Sperm competition and its evolutionary consequences in the insects. Biol Rev Cambr Phil Soc 45:525-567.[CrossRef]
Parker GA, 1982. Why are there so many tiny sperm? Sperm competition and the maintenance of two sexes. J Theor Biol 96:281-294.[CrossRef][Web of Science][Medline]
Parker GA, 1990a. Sperm competition games: raffles and roles. Proc R Soc Lond B 242:120-126.
Parker GA, 1990b. Sperm competition games: sneaks and extrapair copulations. Proc R Soc Lond B 242:127-133.
Parker GA, 1998. Sperm competition and the evolution of ejaculates: towards a theory base. In: Sperm competition and sexual selection (Birkhead TR, Møller AP, eds). London: Academic Press; 154.
Parker GA, Ball MA, Stockley P, Gage MJG, 1996. Sperm competition games: Individual assessment of sperm competition intensity by group spawners. Proc R Soc Lond B 263:1291-1297.
Parker GA, Ball MA, Stockley P, Gage MJG, 1997. Sperm competition games: a prospective analysis of risk assessment. Proc R Soc Lond B 264:1793-1802.[Medline]
Peden AE, 1972. The function of gonopodial parts and behavioral pattern during copulation by Gambusia (Poeciliidae). Can J Zool 50:955-968.[CrossRef]
Petersen CW, 1990. Variation in reproductive success and gonadal allocation in the simultaneous hermaphrodite, Serranus fasciatus. Oecologia 83:62-67.[CrossRef][Web of Science]
Petersen CW, Warner RR, 1998. Sperm competition in fishes. In: Sperm competition and sexual selection (Birkhead TR, Møller AP, eds). London: Academic Press; 435463.
Pilastro A, Bisazza A, 1999. Insemination efficiency of two alternative male mating tactics in the guppy (Poecilia reticulata). Proc R Soc Lond B 266:1887-1891.
Pilastro A, Giacomello E, Bisazza A, 1997. Sexual selection for small size in male mosquitofish (Gambusia holbrooki). Proc R Soc Lond B 264:1125-1129.
Pizzari T, Birkhead TR, 2000. Female feral fowl eject sperm of subdominant males. Nature 405:787-789.[CrossRef][Medline]
Robertson DR, Warner RR, 1978. Sexual patterns in the labroid fishes of the Western Caribbean, II. The parrotfishes (Scaridae). Smiths Contrib Zool 255:1-26.
Shapiro DY, Marconato A, Yoshikawa T, 1994. Sperm economy in a coral reef fish, Thalassoma bifasciatum. Ecology 75:1334-1344.[CrossRef][Web of Science]
Simmons LW, Craig M, Llorens T, Schinzig M, Hosken DJ, 1993. Bushcricket spermatophores vary in accord with sperm competition and parental investment theory. Proc R Soc Lond B 251:183-186.
Simmons LW, Kvarnemo C, 1997. Ejaculate expenditure by male bushcrickets decreases with sperm competition intensity. Proc R Soc Lond B 264:1203-1208.
Simmons LW, Siva-Jothy MT, 1998. Sperm competition in insects: mechanisms and the potential for selection. In: Sperm competition and sexual selection (Birkhead TR, Møller AP, eds). San Diego, California: Academic Press; 341434.
Snelson FF, 1989. Social and environmental control of life history traits in poeciliid fishes. In: Ecology and evolution of livebearing fishes (Poeciliidae) (Meffe GK, Snelson FF, eds). Englewood Cliffs, New Jersey: Prentice Hall; 149161.
Stockley P, Gage MJG, Parker GA, Møller AP, 1997. Sperm competition in fishes: the evolution of testis size and ejaculate characteristics. Am Nat 149:933-954.[CrossRef][Web of Science][Medline]
Warner RR, Robertson DR, 1978. Sexual patterns in the labroid fishes of the Western Caribbean, I. The wrasses (Labridae). Smiths Contrib Zool 254:1-24.
Zane L, Nelson WS, Jones AG, Avise JC, 1999. Microsatellite assessment of multiple paternity in natural populations of a live bearing fish, Gambusia holbrooki. J Evol Biol 12:61-69.
Zulian E, Bisazza A, Marin G, 1995. Variations in male body size in natural populations of Gambusia holbrooki. Ethol Ecol Evol 7:1-10.
![]()
CiteULike
Connotea
Del.icio.us What's this?
This article has been cited by other articles:
![]() |
B. B. M. Wong and M. McCarthy Prudent male mate choice under perceived sperm competition risk in the eastern mosquito fish Behav. Ecol., March 1, 2009; 20(2): 278 - 282. [Abstract] [Full Text] [PDF] |
||||
![]() |
R. Riesch, I. Schlupp, and M. Plath Female sperm limitation in natural populations of a sexual/asexual mating complex (Poecilia latipinna, Poecilia formosa) Biol Lett, June 23, 2008; 4(3): 266 - 269. [Abstract] [Full Text] [PDF] |
||||
![]() |
M. Plath, A. M. Makowicz, I. Schlupp, and M. Tobler Sexual harassment in live-bearing fishes (Poeciliidae): comparing courting and noncourting species Behav. Ecol., July 1, 2007; 18(4): 680 - 688. [Abstract] [Full Text] [PDF] |
||||
![]() |
A. S. Aspbury Sperm competition effects on sperm production and expenditure in sailfin mollies, Poecilia latipinna Behav. Ecol., July 1, 2007; 18(4): 776 - 780. [Abstract] [Full Text] [PDF] |
||||
![]() |
S. A. Ramm and P. Stockley Ejaculate allocation under varying sperm competition risk in the house mouse, Mus musculus domesticus Behav. Ecol., March 1, 2007; 18(2): 491 - 495. [Abstract] [Full Text] [PDF] |
||||
![]() |
S. Awata, D. Heg, H. Munehara, and M. Kohda Testis size depends on social status and the presence of male helpers in the cooperatively breeding cichlid Julidochromis ornatus Behav. Ecol., May 1, 2006; 17(3): 372 - 379. [Abstract] [Full Text] [PDF] |
||||
![]() |
M. Scaggiante, M. B. Rasotto, C. Romualdi, and A. Pilastro Territorial male gobies respond aggressively to sneakers but do not adjust their sperm expenditure Behav. Ecol., November 1, 2005; 16(6): 1001 - 1007. [Abstract] [Full Text] [PDF] |
||||
![]() |
I Schlupp and M Plath Male mate choice and sperm allocation in a sexual/asexual mating complex of Poecilia (Poeciliidae, Teleostei) Biol Lett, June 22, 2005; 1(2): 169 - 171. [Abstract] [Full Text] [PDF] |
||||
| ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||




