Abstract
The roles of male and food density in regulating female performance were investigated in the brackish cladoceran, Daphniopsis australis. Parthenogenetic females and ephippial females were tested using a 2 × 4 factorial experiment involving the presence and the absence of a male cross-classified with nil, low, medium and high food densities. For parthenogenetic females, the male presence and food density failed to trigger the switch from asexual to sexual reproduction, but the presence of male negatively affected parthenogenesis through egg abortion. Food density affected the animal longevity but depended on the male presence. The reproductive output was favoured by increasing food densities, but the male presence increased egg abortion, suggesting male being an added stress factor to parthenogenetic females. For ephippial females, food densities affected the frequency of switch from sexual to asexual modes in the absence and the presence of a male. However, the male enhanced switch frequency under low and high food densities. Longevity was increased with the male presence but was unaffected by food density. The ephippial females successfully produced diapausing eggs with the male presence. Although, ephippial females could switch to parthenogenesis but the reproductive output of switched ephippial females was inferior to that of parthenogenetic females since birth. The results reveal that the male presence and food density can impact the performance of female D. australis. Hence, this study provides an insight into the understanding of the reproductive biology of cladocerans and a possible alternative explanation for population dynamic of this species and other cladocerans in the field.
Similar content being viewed by others
Avoid common mistakes on your manuscript.
Introduction
Parthenogenesis is a typical reproductive mode in cladoceran life history (De Meester et al., 2004). Under favourable conditions of food, temperature, and low population density, parthenogenesis is the prevailing mode of reproduction in cladocerans (Shan, 1969; Gilbert & Williamson, 1983) and enables fast population growth (Shrivastava et al., 1999) and rapid resource exploitation (Tomlinson, 1966). However, when the environmental conditions become unfavourable, parthenogenetic females can switch to sexual reproduction through the production of ephippial females (Gilbert & Williamson, 1983). In sexual reproduction, females parthenogenetically produce a brood containing diploid males, and the ephippial females that produce haploid diapausing eggs to be fertilised by a male (Innes & Singleton, 2000). Diapausing eggs are protected by a modified carapace known as ephippium and are resistant to freezing and desiccation conditions (Berg et al., 2001). Under adverse conditions, males are produced earlier than sexual females (Larsson, 1991; Dole-Olivier et al., 2000), and the productions of males and ephippial females are independent events (Hobaek & Larsson, 1990).
In a parthenogenetic population, females are able to switch from an asexual mode to a sexual mode of reproduction and vice versa depending on environmental factors. Among these factors, food availability is essential because it supplies nutrients for egg formation (Vijverberg, 1989). With abundant food supply, parthenogenetic females usually dominate the population and subsequently expand the size of the population through asexual reproduction by exploiting available resources. However, under starvation, females can switch from a parthenogenetic mode to an ephippial mode for sexual reproduction (D’Abramo, 1980). The sexual reproduction is considered successful after the ephippial female mates with a male and starts to produce diapausing eggs.
The switch of reproductive modes in a female cladoceran has been considered an adaptation to survive in harsh conditions (Bunner & Halcrow, 1977). Besides food availability, changes in photoperiod, temperature and population density also trigger the switch from asexual to sexual reproduction (Banta et al., 1939; Berner et al., 1991; Kleiven et al., 1992). Among these proximate factors, the initiation of sexual reproduction seems to be more responsive to the changes in population density (Innes, 1997) and food availability than other factors (Gibson et al., 1998; Martinez-Jeronimo et al., 2007). Nevertheless, despite the fact that the male is the key element in sexual reproduction, little is still known on its role in regulating cladoceran reproduction.
In a pioneer study, Banta et al. (1939) reported that male presence may not lead to a change in reproductive mode in females when food is abundant. The early production of males is believed to represent a wasteful evolutionary strategy, particularly when these males could not find any sexual females to copulate with (Larsson, 1991). Some studies have demonstrated that males usually appear prior to the ephippial females (Stirling & McQueen, 1986; Schwartz & Hebert, 1987) and that the presence of males may stimulate the production of ephippial females (Innes, 1997). Clearly, these observations suggest that the male may play a role to switch the modes of reproduction in females, and this impact might depend on food availability.
The genus Daphniopsis is classified under the family of Daphniidae (Cladocera) (Benzie, 2005), and is globally distributed in saline waters in Asia (Sars, 1903), Australia (Sergeev & Williams, 1985), North America (Schwartz & Hebert, 1987) and South America (Hann, 1986). More specifically, Daphniopsis australis has been found in brackish waters with salinities of 4–30 PSU (Sergeev & Williams, 1985). Previous studies on D. australis have focused on systematics (Colbourne et al., 2006), diversity (Hebert & Wilson, 2000) and osmoregulation (Aladin & Potts, 1995). However, to our knowledge, information on the reproductive biology of brackish cladocerans is still rare. This study aimed (i) to test whether the presence of a male impacts the reproductive mode of parthenogenetic and ephippial females of D. australis and (ii) to investigate the interactive effect of the male and food density on the mode of female reproduction.
Materials and methods
Stock culture conditions
Experimental animals, D. australis, were collected from a saline water pond (22 PSU) in the Coorong National Park, South Australia. All the collected individuals (ca. 100 parthenogenetic females) were used to start a static culture in 10-l plastic containers. This method has been used in population dynamic studies of other zooplanktonic taxa (Nandini & Rao, 1997; Nandini & Sarma, 2002). The experimental population has been maintained for over 100 generations in our laboratory since 2005. The rearing medium was prepared using filtered seawater diluted with demineralised water to obtain the desired salinity 22–23 PSU. Animals were fed with microalgae Isochrysis tahitian at a density of 106 cells/ml, which is in the optimal range for most Daphniidae species (Delbare & Dhert, 1996). The food was given every other day. Environmental variables were controlled at a photoperiod of 12 h light and 12 h dark with a light intensity of 1800 Lux at 20–22°C. In order to avoid overcrowding and population crash, the population density was controlled at <1000 ind/l in the stock culture. Prior to the experiment, an allozyme analysis was conducted to test the genetic diversity and clonal structure of 20 randomly chosen animals. The allozyme data for 35 putative loci showed that these animals belonged to a single genetic clone.
The life cycle of D. australis
Through the allozyme analysis, the authors confirmed that the D. australis population was derived from the progenies of cyclic parthenogenesis consisting of an alternation of an asexual phase and a sexual phase. In the rearing environment, the asexual phase occurred in a condition similar to the stock culture. During the asexual phase, only female individuals were produced through parthenogenesis. From birth to sexual maturation, a female took 6–7 days with four to five juvenile instars to reach maturity. Adult parthenogenetic females could reproduce approximately 10–12 clutches in the life time with embryonic development of 3–4 days. Upon reaching the senescent stage, the reproduction usually ceased, and the female continued to live with an empty brood chamber until death. The life span of a parthenogenetic female ranged 20–30 days but on a rare occasion, some of females lived up to 60 days.
The sexual phase occurred under unfavourable culture conditions and was triggered by low food density and overcrowding when temperature, salinity and photoperiod were set up at 20–22°C, 22–23 PSU and 12 h light and 12 h dark, respectively. During the sexual phase, parthenogenetic females produce a brood carrying either diploid males or females (Innes, 1997), and some of these females are able to transform into sexual females. The sexual female carrying an ephippium was called an ephippial female. Both the male and ephippial female individuals were involved in a mating process, and the fertilised sexual eggs would then develop into diapausing eggs. The ephippial female of D. australis could produce a maximum of two diapausing eggs which were encased in an ephippium and detached from the mother during moulting. During our observations, ephippial females usually were formed in the parthenogenetic mode, and an ephippium was produced before the sexual eggs were released. In addition, ephippial females appeared only for a short period because they would die soon after releasing the ephippium. Thus, the lifespan of ephippial females is much shorter than that of the parthenogenetic females.
Experimental design and procedure
Parthenogenetic females
The maternal effect carried over generations by a parthenogenetic female was eliminated through the experimental procedure (Lynch & Ennis, 1983). A single parthenogenetic female was isolated into a single jar containing 50-ml culture medium until the first generation was born. Neonates were then individually transferred into a new jar containing 50-ml of fresh medium for acclimatisation at low, medium and high food densities. As the media were daily renewed, the animals were allowed to continue breeding in the corresponding food densities until the third generation. Only animals from third generation were used for testing the female reproductive performance. Since proliferation under nil food supply was unlikely, experimental animals were taken among cohorts reproduced under the low food density. Meanwhile, for male production, some of the culture containers were treated with a combination of low food density (<105 Isochrysis/ml) and overcrowding (>1000 ind/l) to simulate an adverse environment (Kleiven et al., 1992).
The reproductive responses of parthenogenetic females to the presence or the absence of a male were separately examined under different food densities. Microalgae (I. tahitian) were used at four densities to represent high (2 × 106 cells/ml), medium (1 × 106 cells/ml), low (0.5 × 106 cells/ml) and nil food supply. The selection of algal densities was based on the literature data on food requirements for daphniid and non-daphniid species (Nandini & Sarma, 2003; Nandini et al., 2009). Adult individuals were selected for this study because they could be differentiated between asexual and sexual modes. Parthenogenetic females were 6–7 day old (i.e. the age at first reproduction). Parthenogenetic females were individually inoculated in a jar containing 50-ml medium with nil, low, medium, high food densities. Then, one male was introduced into each container as the male treatment. In the non-male treatment, two parthenogenetic females were inoculated to equalise the animal density. Each treatment was replicated 25 times, and the culture medium was daily renewed. The females were checked daily under a stereomicroscope for sexual switch between asexual and sexual reproductive modes (%), longevity (day), egg production (egg/female) and offspring production (offspring/female). Abortion frequency (%) was also recorded when premature embryos were released from the brood chamber. Any newly hatched neonates were enumerated and immediately removed to offset the crowding effect. Other environmental factors such as temperature, salinity and photoperiod were controlled at the same condition as the animals in the stock culture.
Ephippial females
In the stock culture, three food densities were used to reduce the confounding factors when the animals were transferred to the three respective food densities in the experimental trial. The ephippial females were randomly chosen from the culture containers at each food density. According to the culture history, the ephippial females were over 15 days old. The production of ephippial females in the containers occurred when the density of animals reached >1000 individual/ml in each container. The responses of ephippial females to the presence or the absence of a male under various food densities were tested in the similar protocol as for the parthenogenetic females. Ephippial females were examined for switch frequency from sexual to asexual mode (%), longevity (day), parthenogenetic egg production (egg/female), parthenogenetic offspring production (offspring/female) and diapausing egg production (egg/female). In order to ensure the production of authentic diapausing eggs, each ephippium was checked using a stereomicroscope under 20× magnifications. Any empty ephippium was excluded from the counts. Experiments were continued until all the females had died naturally.
Statistical analysis
The impacts of male and food density on parthenogenetic and ephippial females were tested separately. The abortion and switch frequencies were analysed using G-test for goodness-of-fit (Sokal & Rohlf, 1995). Other variables were analysed using two-way ANOVA. In order to interpret the strength between the independent variables, we compared the size effect using Partial Eta Squared test (partial η2) (Leech et al., 2008). In the parthenogenetic female trial, a square root transformation was used for egg production and total number of offspring to abide by the assumption for variance analysis. A post-hoc comparison was conducted using Tukey HSD test when the significance of the main effects or their interactions were at P < 0.05.
In the ephippial female trial, two-way ANOVA was employed, and Tukey HSD test was conducted for post-hoc tests. Inverse transformation was used for data on the number of parthenogenetic eggs to satisfy the normality assumption. In post-hoc comparisons, the non-parametric Games–Howell test was used when data significantly showed heteroscedasticity (Leech et al., 2008). However, in the analysis for the diapausing eggs and parthenogenetic offspring, we dropped the male factor from the two-way ANOVA model because it did not produce any impact. Thus, one-way ANOVA and Games–Howell tests were used to examine the effect of food densities on these two variables. The level of significant differences was also set at P < 0.05.
Results
Parthenogenetic females
We followed each animal until its death, but the physiological status varied between treatments. When the male was present, the percentages of dead females carrying eggs at nil, low, medium and high food densities were for 44, 32, 52 and 56%, respectively. Likewise, in the absence of a male, the percentages of dead females carrying eggs were 20, 32, 72 and 68% with respect to food densities.
Reproductive mode and abortion
None of the parthenogenetic females switched to a sexual mode of reproduction. All parthenogenetic females stayed in an asexual mode until death but the females aborted their eggs at the medium and high food densities (Fig. 1a). At high food density, the abortion frequency was significantly higher in the presence of a male than without a male (G-Test; P < 0.05; Table 1) while the impact of male presence was insignificant at the medium food density (P > 0.05; Table 1). In contrast, in the presence of a male, the abortion frequency significantly increased when the food density changed from medium to high levels (P < 0.05; Table 1), but the abortion frequency was unaffected by the food density in the absence of a male (P > 0.05; Table 1). Abortion did not occur in parthenogenetic females under nil food or low food density, regardless of the male factor (Fig. 1a).
Longevity
In parthenogenetic females, there was a significant effect of food density, male presence and their interaction (two-way ANOVA; P = 0.001; Table 2). The impact of food (partial η2 = 0.480) on longevity was stronger than the male (partial η2 = 0.216; Table 2). The longest longevity occurred at low food and medium food densities (Tukey HSD; P < 0.05; Fig. 1b) regardless of the male factor. The female longevity decreased in the absence of food, but at the low and high food densities, the presence of a male significantly reduced the female longevity (P < 0.05; Fig. 1b).
Egg production
In parthenogenetic females, there was a significant interactive effect between the male and food treatments on egg production (two-way ANOVA; P = 0.001; Table 2), with food density (partial η2 = 0.749) producing a stronger impact than the male (partial η2 = 0.231; Table 2). Irrespective of the male, the egg production was higher at the medium food density than other food densities (Tukey HSD; P < 0.05; Fig. 1c). Male presence significantly reduced the egg production in the nil food and medium food densities (P < 0.05; Fig. 1c), but did not affect the egg production in the low and high food densities (P > 0.05; Fig. 1c).
Offspring production
The pattern of offspring production (Fig. 1d) was similar to that of egg production in parthenogenetic females (Fig. 1c). There was a significant interactive effect between the male and food density on the production of offspring (two-way ANOVA; P = 0.001; Table 2), with food (partial η2 = 0.835) having a stronger impact than the male (partial η2 = 0.397). The highest offspring production occurred at the medium food density, but the male presence significantly reduced offspring production (Tukey HSD; P < 0.05; Fig. 1d). Similarly, the presence of a male significantly suppressed the production of offspring in the nil food regime (P < 0.05; Fig. 1d), but had no impact at low and high food densities.
Ephippial females
Although each animal was followed until death, the physiological performance of the females differed between treatments. When the male was present, the percentages of dead females carrying an ephippium at nil, low, medium and high food densities were 96, 28, 80 and 48%, respectively. Likewise, in the absence of a male, the percentages of dead females carrying an ephippium at the above food density levels were 96, 88, 72 and 92%, respectively.
Reproductive mode
Ephippial females switched from the sexual mode to the asexual mode (Fig. 2a). The switch frequency of ephippial females was significantly higher in the male presence than the male absence at low and high food densities (G-Test; P < 0.05; Table 3). Meanwhile, the presence of a male did not affect switch frequencies at nil food and medium food densities (P > 0.05; Table 3). Disregarding the male, food density significantly affected the sex switch frequency (P < 0.05; Table 3).
Longevity
The effect of male on the longevity of ephippial females was related to food densities (two-way ANOVA; P = 0.001; Table 4) with a stronger contribution of the male (partial η2 = 0.222) than the food densities (partial η2 = 0.037). In contrast, there was no significant difference in longevity between food densities (two-way ANOVA; P = 0.063). In the presence of a male, the longevity of ephippial females in the absence of food was significantly higher than that at low and medium food densities (Tukey HSD; P < 0.05; Fig. 2b). In the absence of a male, the longevity of ephippial females was not significantly affected by food density (P > 0.05; Fig. 2b).
Egg production
The switched ephippial female referred to an asexual female that was switched from an ephippial female. There was no significant interactive effect between male and food on the production of parthenogenetic eggs in the switched ephippial females (two-way ANOVA; P = 0.487; Table 4). However, the male presence significantly enhanced the production of parthenogenetic eggs (ANOVA; P = 0.001) under low and high food densities (Games–Howell test; P < 0.05; Fig. 2c). The impact of the male on egg production was not detected under nil and medium food densities (P > 0.05; Fig. 2c).
Diapausing eggs were only produced by ephippial females in the presence of a male, regardless of food densities (Fig. 2d). However, there was a significant difference in the number of diapausing eggs produced between food densities (one-way ANOVA; P = 0.001; Table 5). Diapausing egg production was significantly lower at the medium food density than at other food densities (Games–Howell test; P < 0.05; Fig. 2d), but no difference was detected between the nil, low and high food densities (Games–Howell test; P > 0.05; Fig. 2d).
Parthenogenetic offspring production
In the switched ephippial females, the production of parthenogenetic offspring was affected by the food density (one-way ANOVA; P = 0.001; Table 5). More progenies were produced at low and high food densities than at medium and nil food densities (Games–Howell test; P < 0.05; Fig. 2e).
Discussion
When D. australis entered a sexual phase, the presence of a male is required for mating. In other cladoceran species, the male usually appears prior to the emergence of the ephippial female (Shan, 1969; Stirling & McQueen, 1986; Schwartz & Hebert, 1987). The early appearance of males may stimulate the production of ephippial females and thus males are usually produced before food becomes limited (Innes, 1997). Under this scenario, the presence of males may trigger the switch of females from an asexual to a sexual mode of reproduction, regardless of food conditions. However, in this study, male presence did not change the reproductive mode of asexual female.
Impact of male and food on parthenogenetic females
In our study, no parthenogenetic females switched to ephippial females in any treatments. Instead, all the parthenogenetic females remained in an asexual mode until death. This contradicts the notion that male presence could trigger females to switch from asexual to sexual reproduction (Innes, 1997). Martinez-Jeronimo et al. (2007) reported that the number of males that trigger the sexual reproduction accounted for 6–56% in a cladoceran population, a result consistent with the proportion of males (50%) observed in this study. Despite the lack of switch in reproductive mode, we found that parthenogenetic females showed higher egg abortion at high food density in the presence of a male than that without the male. Abortion in parthenogenetic females can be caused by high temperature (Chen & Folt, 1996), toxic metabolic products (Marques et al., 2004) and low food quality (Urabe & Sterner, 2001). Our study shows that the presence of a male mediated with food supply can also induce female abortion.
The mating behaviour of a male typically starts from pursuing (and eventually copulating with) a female (Damme & Dumont, 2006). We found herein that the male D. australis repeatedly approached a parthenogenetic female in an attempt to mate, while the parthenogenetic female consistently refused copulation through escaping. This escape mechanism has been observed in other cladoceran species such as Chydorus sp. (Damme & Dumont, 2006), Daphnia sp. (Winsor & Innes, 2002) and Moina sp. (Forro, 1997), but these studies did not report on the impact of males on the reproductive biology of females. The escape behaviour of parthenogenetic females indicates that the female is not sexually receptive. The constant harassment by a male on an ovigerous female may, however, have led to egg abortion. The abortion rate reached the maximum at the high food density because adequate food facilitated the formation of new clutch of eggs but did not change the magnitude of stress from the mating attempts by a male. However, any stress due to the presence of a male is not strong enough to trigger the production of ephippial females, despite the presence of the male consequently affecting the development of parthenogenesis. This finding implies a unique role of the male in the reproductive biology of female D. australis. While the presence of a male is necessary for sexual reproduction, the male presence may also exert adversely impact on the asexual reproduction.
The presence of a male also affected the longevity and reproductive performance of parthenogenetic females, though this impact was dependent on food density. In general, the longevity of a female was significantly enhanced in the presence of food, but the presence of a male reduced female longevity, especially at the low and high food densities. Furthermore, parthenogenetic females produced fewer eggs and offspring in the presence than the absence of a male. It seems that the presence of a male can be an unfavourable factor for asexual reproduction in female and the persistent mating attempts by a male can negatively impact the reproductive output of parthenogenetic females. Therefore, the male presence can induce a considerable amount of stress and consequently reduce the longevity and fitness of parthenogenetic females.
Besides male presence, food availability alone is a cue for switching the reproductive mode in parthenogenetic animals (Carvalho & Hughes, 1983). In response to food availability, the parthenogenetic populations typically switch from an asexual mode to sexual mode in Daphnia magna (Carvalho & Hughes, 1983) and Moina macrocopa (D’Abramo, 1980). This is an important adaptation to preserve a population over harsh environments (Gyllstrom & Hansson, 2004). However, the population of D. australis does not display such a strategy in response to a reduction of food supply in the absence of a male. A similar pattern was also reported in Daphniopsis studeri from Antarctica (Gibson et al., 1998) suggesting that food density is not the only cue to induce the switch from asexual to sexual reproduction.
Under the laboratory condition, we demonstrated that male presence reduced an individual’s fitness as measured by abortion of parthenogenetic eggs plus reduction in longevity, whereas food availability increased female fitness. At low food supply, females lived longer with compromised sexual reproductive output. The vulnerability of female D. australis to food availability and male interference may provide a new insight into the understanding of seasonal succession and population dynamics of this species in nature. However, the relative importance of male and food availability in a natural population may vary, given the complex interactions of other ecological factors in the field. Therefore, the implications of our laboratory results of the population dynamics of D. australis to a natural population in the field warrant further study.
Impact of male and food on ephippial female
Parthenogenesis is an adaptive strategy of reproduction under favourable conditions (De Meester et al., 2004). However, it is not clear whether the ephippial female can switch back to parthenogenesis when the condition becomes favourable. When meiosis is involved, returning to a mitotic mode of reproduction may be difficult (Corley & Moore, 1999). In this study, we found that D. australis was able to switch from a sexual mode to an asexual mode of reproduction. However, the driving mechanisms are still unclear, and further investigations would be needed to assess this specific issue. Switches also occurred under nil and medium food densities, but this incidence was regulated by the male presence. It seems that the switch of reproductive mode is more sensitive to the male presence in food-constrained females than in non-food-constrained females. Our data suggest that the switch from the sexual mode to asexual mode is more likely under a synergistic effect of unfavourable food supply and male presence.
In this study, the sex switches under unfavourable food conditions were coupled with the male presence. The switch by an ephippial female to a parthenogenetic mode may provide a greater opportunity to produce more progeny than switching to a male (Lynch, 1989). However, in the absence of a male, this reproductive strategy was not observed under low food density. It seems that the male presence is likely to trigger the switch from the sexual mode to an asexual mode in the ephippial female. The active role of male in sexual reproduction was coupled with the behaviour of avoiding mating in ephippial females, implying that the mating pressure from a male may stress the ephippial female and this stress could facilitate the change of reproductive mode. To our knowledge, this study was the first to report that male interference can stimulate an ephippial female to switch to a parthenogenetic mode.
In such cases, ephippial females generally lived longer in the presence of a male. Usually, the ephippial females of this species produce a maximum of two diapausing eggs in sexual reproduction (Sergeev & Williams, 1985). Ephippial females will produce an empty ephippium when the male is absent (Winsor & Innes, 2002). In our study, diapausing eggs were only found in ephippial females in the presence of a male. The total number of diapausing eggs produced by ephippial D. australis in a lifetime was never more than two, suggesting that every mating effort does not always lead to the production of diapausing eggs. The reason why the second cycle of sexual reproduction was missing was probably because the ephippial females either died or switched to an asexual mode of reproduction after the first cycle of diapausing egg production.
Regarding food densities, ephippial female D. australis displayed a high frequency of switching at an abundant food supply. This result was not surprising since parthenogenesis usually prevails under abundant food conditions in the life cycle of parthenogenetic animals (Gilbert & Williamson, 1983). The switch from sexual to asexual reproduction is also demonstrated by Pleuroxus denticulatus (Shan, 1969) and D. magna (Zhang & Baer, 2000). The restoration to parthenogenesis in the ephippial females in both populations was not only due to food availability but also in response to chemical stimuli. In our study, the switch of D. australis to parthenogenesis at abundant food could be a strategy to exploit food resource and such a switch consequently increased the reproductive output through parthenogenetic reproduction. However, as ephippial females have a short lifespan, the short longevity limits the duration of asexual reproduction.
In conclusion, the role of males in abortion and in the switching of reproductive mode provides a new and alternative explanation to the population dynamics of cladocerans. The male presence increased egg abortion in parthenogenetic female. The switched ephippial females only produced parthenogenetic females, but did not produce males. Parthenogenetic females failed to produce ephippial females, suggesting that more complex factors regulate the formation of ephippial eggs in female D. australis. The intermediate result of ephippial formation did not occur in the medium food density, indicating that food itself is not the only determinant for ephippial formation.
References
Aladin, N. V. & W. T. W. Potts, 1995. Osmoregulatory capacity of the Cladocera. Journal of Comparative Physiology B: Biochemistry Systematic Environmental Physiology 164: 671–683.
Banta, A. M., T. R. Wood, L. A. Brown & L. Ingle, 1939. Studies on the Physiology, Genetics, and Evolution of Some Cladocera. Carnegie Institution of Washington, Washington.
Benzie, J. A. H., 2005. The Genus Daphnia (Including Daphniopsis) Anomopada: Daphniidae. Kenobi Productions, Ghent.
Berg, L. M., S. Palsson & M. Lascoux, 2001. Fitness and sexual response to population density in Daphnia pulex. Freshwater Biology 46: 667–677.
Berner, D. B., L. Nguyen, S. Nguy & S. Burton, 1991. Photoperiod and temperature as inducers of gamogenesis in a dicyclic population of Scapholeberis armata Herrick (Crustacea, Cladocera, Daphniidae). Hydrobiologia 225: 269–280.
Bunner, H. C. & K. Halcrow, 1977. Experimental inductions of the production of ephippia in Daphnia magna Straus. Crustaceana 32: 77–86.
Carvalho, G. R. & R. N. Hughes, 1983. The effect of food availability, female culture-density and photoperiod on ephippia production in Daphnia magna Straus (Crustacea: Cladocera). Freshwater Biology 13: 37–46.
Chen, C. Y. & C. L. Folt, 1996. Consequences of fall warming for zooplankton overwintering success. Limnology Oceanography 41: 1077–1086.
Colbourne, J. K., C. C. Wilson & P. D. N. Hebert, 2006. The systematics of Australian Daphnia and Daphniopsis (Crustacea: Cladocera): a shared phylogenetic history transformed by habitat-specific rates of evolution. Biological Journal of the Linnean Society 89: 469–488.
Corley, L. S. & A. J. Moore, 1999. Fitness of alternative modes of reproduction: developmental constraints and the evolutionary maintenance of sex. Proceedings of the Royal Society B Biological Sciences 266: 471.
D’Abramo, L., 1980. Ingestion rate decrease as the stimulus for sexuality in populations of Moina macrocopa. Limnology and Oceanography 25: 422–429.
Damme, K. V. & H. J. Dumont, 2006. Sex in a cyclical parthenogen: mating behaviour of Chydorus sphaericus (Crustacea; Branchiopoda; Anomopoda). Freshwater Biology 51: 2334–2346.
De Meester, L., A. Gomez & J. C. Simon, 2004. Evolutionary and ecological genetics of cyclical parthenogens. In Moya, A. & E. Font (eds), Evolution: From Molecules to Ecosystems. Oxford University Press, New York.
Delbare, D. & P. Dhert, 1996. Cladocerans, nematodes and trochophora. In Laverns, P. & P. Sorgeloos (eds), Manual on the Production and Use of Live Food for Aquaculture. Food and Agriculture Organization of United Nation, Rome.
Dole-Olivier, M. J., D. M. P. Galassi, P. Marmonier & M. C. Des Chatelliers, 2000. The biology and ecology of lotic microcrustaceans. Freshwater Biology 44: 63–91.
Forro, L., 1997. Mating behaviour in Moina brachiata (Jurine, 1820) (Crustacea, Anomopoda). Hydrobiologia 360: 153–159.
Gibson, J. A. E., H. J. G. Dartnall & K. M. Swadling, 1998. On the occurence of males and production of ephippial eggs in populations of Daphniopsis studeri (Cladocera) in lakes of the Vestfold and Larsemann Hills, East Antarctica. Polar Biology 19: 148–150.
Gilbert, J. J. & C. E. Williamson, 1983. Sexual dimorphism in zooplankton (Copepoda, Cladocera, and Rotifera). Annual Review of Ecology, Evolution, and Systematics 14: 1–33.
Gyllstrom, M. & L. A. Hansson, 2004. Dormancy in freshwater zooplankton: induction, termination and the importance of benthic-pelagic coupling. Aquatic Sciences 66: 274–295.
Hann, B. J., 1986. Revision of the genus Daphniopsis Sars 1903 (Cladocera: Daphnidae) and a description of Daphniopsis chilensis, a new species from South America. Journal of Crustacean Biology 6: 246–263.
Hebert, P. D. N. & C. C. Wilson, 2000. Diversity of the genus Daphniopsis in the saline waters of Australia. Canadian Journal of Zoology 78: 794–808.
Hobaek, A. & P. Larsson, 1990. Sex determination in Daphnia magna. Ecology 71: 2255–2268.
Innes, D. J., 1997. Sexual reproduction of Daphnia pulex in a temporary habitat. Oecologia 111: 53–60.
Innes, D. J. & D. R. Singleton, 2000. Variation in allocation to sexual and asexual reproduction among clones of cyclically parthenogenetic Daphnia pulex (Crustacea: Cladocera). Biological Journal of the Linnean Society 71: 771–787.
Kleiven, O. T., P. Larsson & A. Hobaek, 1992. Sexual reproduction in Daphnia magna requires 3 stimuli. Oikos 65: 197–206.
Larsson, P., 1991. Intraspecific variability in response to stimuli for male and ephippia formation in Daphnia pulex. Hydrobiologia 225: 281–290.
Leech, N. L., K. C. Barrett & G. A. Morgan, 2008. SPSS for Intermediate Statistic: Uses and Interpretation, 3rd ed. Taylor & Francis Group, New York.
Lynch, M., 1989. Life-history consequences of resource depression in Daphnia pulex. Ecology 70: 246–256.
Lynch, M. & R. Ennis, 1983. Resource availability, maternal effects, and longevity. Experimental Gerontology 18: 147–165.
Marques, C. R., N. Abrantes & F. Gonçalves, 2004. Life-history traits of standard and autochthonous cladocerans: II. Acute and chronic effects of acetylsalicylic acid metabolites. Environmental Toxicology 19: 527–540.
Martinez-Jeronimo, F., J. Rodriguez-Estrada & R. Villasenor-Cordova, 2007. Effect of culture density and volume on Moina micrura (Kurz, 1874) reproduction, and sex ratio in the progeny. Hydrobiologia 594: 69–73.
Nandini, S., M. Silva-Briano, G. G. García, S. S. S. Sarma, A. Adabache-Ortiz & R. G. de la Rosa, 2009. First record of the temperate species Daphnia curvirostris Eylmann, 1887 emend. Johnson, 1952 (Cladocera: Daphniidae) in Mexico and its demographic characteristics in relation to algal food density. Limnology 10: 87–94.
Nandini, S. & T. R. Rao, 1997. Somatic and population growth in selected cladoceran and rotifer species offered the cyanobacterium it Microcystis aeruginosa as food. Aquatic Ecology 31: 283–298.
Nandini, S. & S. S. S. Sarma, 2002. Competition between Moina macrocopa and Ceriodaphnia dubia: a life table demography study. International Review of Hydrobiology 87: 85–95.
Nandini, S. & S. S. S. Sarma, 2003. Population growth of some genera of cladocerans (Cladocera) in relation to algal food (Chlorella vulgaris) levels. Hydrobiologia 491: 211–219.
Sars, G. O., 1903. On the crustacean fauna of Central Asia. 2. Cladocera. Ezhegodnik Zoologicheskogo Muzeia Imperatorskoi Akademii Nauk 8: 157–194.
Schwartz, S. S. & P. D. N. Hebert, 1987. Breeding system of Daphniopsis ephemeralis: adaptation to a transient environment. Hydrobiologia 145: 195–200.
Sergeev, V. & W. D. Williams, 1985. Daphniopsis australis nov. sp. (Crustacea: Cladocera), a further daphniid in Australian salt lakes. Hydrobiologia 120: 119–128.
Shan, R. K., 1969. Life cycle of a chydorid cladoceran, Pleuroxus denticulus Birge. Hydrobiologia 34: 513–523.
Shrivastava, Y., G. G. Mahambre, C. T. Achuthankutty, B. Fernandes, S. C. Goswami & M. Madhupratap, 1999. Parthenogenetic reproduction of Diaphanosoma celebensis (Crustacea: Cladocera). Effect of algae and algal density on survival, growth, life span and neonate production. Journal of Marine Biology 135: 663–670.
Sokal, R. R. & F. J. Rohlf, 1995. Biometry: The Principle and Practice of Statistics in Biological Research, 3rd ed. W. H. Freeman and Company, New York.
Stirling, G. & D. J. McQueen, 1986. The influence of changing temperature on the life history of Daphniopsis ephemeralis. Journal of Plankton Research 8: 583–595.
Tomlinson, J., 1966. The advantages of hermaphroditism and parthenogenesis. Journal of Theoretical Biology 11: 54–58.
Urabe, J. & R. W. Sterner, 2001. Contrasting effects of different types of resource depletion on life-history traits in Daphnia. Functional Ecology 15: 165–174.
Vijverberg, J., 1989. Culture techniques for studies on the growth, development and reproduction of copepods and cladocerans under laboratory and in situ conditions: a review. Freshwater Biology 21: 317–373.
Winsor, G. L. & D. J. Innes, 2002. Sexual reproduction in Daphnia pulex (Crustacea: Cladocera): observations on male mating behaviour and avoidance of inbreeding. Freshwater Biology 47: 441–450.
Zhang, L. & K. N. Baer, 2000. The influence of feeding, photoperiod and selected solvents on the reproductive strategies of the water flea, Daphnia magna. Environmental Pollution 110: 425–430.
Acknowledgements
This research was partially supported by a Scholarship from Universiti Teknologi MARA Malaysia and Malaysian Ministry of Higher Education. Professor Seuront is the recipient of an Australian Professorial Fellowship (project number DP0988554).
Author information
Authors and Affiliations
Corresponding author
Additional information
Handling editor: P. Spaak
Rights and permissions
About this article
Cite this article
Ismail, H.N., Qin, J.G., Seuront, L. et al. Impacts of male and food density on female performance in the brackish cladoceran Daphniopsis australis . Hydrobiologia 652, 277–288 (2010). https://doi.org/10.1007/s10750-010-0359-8
Received:
Revised:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s10750-010-0359-8