High predation risk and food depletion lead to sexual reproduction in cyclically parthenogenetic Daphnia. Mating, the core of sexual reproduction, also occurs under these conditions. Assessment of the environmental conditions and alteration of mating efforts may aid in determining the success of sexual reproduction. Here, we evaluated the impacts of predation risk, food quantity, and reproductive phase of females on the mating behavior of Daphnia obtusa males including contact frequency and duration using video analysis. Mating–related behavior involved male–female contact (mating) as well as male–male contact (fighting). Mating frequency increased while unnecessary fighting decreased in the presence of predation risk. In addition, low food concentration reduced fighting between males. Males attempted to attach to sexual females more than asexual females, and fighting occurred more frequently in the presence of sexual females. Duration of mating was relatively long; however, males separated shortly after contact in terms of fighting behavior. Thus, assessment of environmental factors and primary sexing of mates were performed before actual contact, possibly mechanically, and precise sex discrimination was conducted after contact. These results suggest that mating in Daphnia is not a random process but rather a balance between predation risk and energetic cost that results in changes in mating and fighting strategies.
Citation: La G-H, Choi J-Y, Chang K-H, Jang M-H, Joo G-J, Kim H-W (2014) Mating Behavior of Daphnia: Impacts of Predation Risk, Food Quantity, and Reproductive Phase of Females. PLoS ONE 9(8): e104545. https://doi.org/10.1371/journal.pone.0104545
Editor: Cheryl S. Rosenfeld, University of Missouri, United States of America
Received: March 20, 2014; Accepted: July 10, 2014; Published: August 11, 2014
Copyright: © 2014 La et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: The authors confirm that all data underlying the findings are fully available without restriction. All data are included within the paper.
Funding: The Korea National Long–Term Ecological Research Program (2011∼2013) by the Ministry of Environment of Korea and postdoctoral program (2011) of the Sunchon National University supported this study. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
Daphnia (Cladocera) exhibit two types of reproductive modes: asexual and sexual. Asexual reproduction is performed under favorable conditions such as low predation pressure and adequate food, and through this reproductive mode, adult females produce clones (both females and males) of themselves without mating . However, sexual reproduction, as an alternative to prevent the extermination of population, is required since Daphnia inhabit changing environments in which high seasonal mortality occurs due to predation as well as food depletion caused by rapidly increasing conspecifics and other zooplankton. Sexual reproduction is triggered in Daphnia populations in response to biological signals, including predation risk mediated by chemicals (kairomones) released by various predators , food shortage, or quality deterioration ,  and crowding of conspecifics . In addition to these biological factors, environmental factors such as temperature  and photoperiod  also promote sexual reproduction.
During sexual reproduction, females produce haploid sexual eggs in their ovaries instead of immediately hatching asexual eggs. In order to develop, sexual eggs must be fertilized through mating, although hatching can be postponed for many years depending on the conditions . Fertilized diploid eggs are enclosed within a dark, protective shell called the ephippium before they are released into the water column. Unfertilized eggs are possibly resorbed and only the empty ephippium is produced . Resting eggs in the ephippium are resistant against harsh conditions such as the digestive enzymes of fish  and drying, although their decreases viability over time . Resting eggs hatch during favorable periods (e.g. spring) and ensure the persistence of the population . In addition, they give rise to genetic diversity in the population by gene recombination .
As a core element of sexual reproduction, mating of cladoceran involves the processes of encounter, grasp, and copulation . Among these, the encounter rate is strongly affected by the population density . In general, males are scarce in parthenogenetic Daphnia populations since the sex ratio is biased toward females. Moreover, Daphnia distribute sparsely in their habitatand have poorly developed eyesight; they can only distinguish changes in light intensity  and detect a limited light spectrum in the turbid water . Thus, both males and sexual females may encounter problems in finding each other due to their limited visual sensory abilities. Daphnia employ several techniques to overcome this. First, as a life history change, the production of large quantities of males during sexual reproduction maximizes efficient mating and reduces critical density for mating , . Further, the ultimate goal of mating in Daphnia is the production of sexually fertilized eggs. For this reason, males occurred 1–2 weeks before sexual females to ensure encounters between receptive females and mature males . Cladocerans, such as Moina affinis  and D. magna  often form swarms (high–density distributions) consisting of both sexes in their habitats. In addition, D. pulicaria  and Bosmina longirostris  exhibit sex–dependent swimming patterns; males swim faster and exhibit scanning behavior to ensure convergence of the swimming tracks of both sexes. Although the major purpose of swarming is suggested to be predation avoidance, these life history and behavioral changes may increase encounters between the sexes. As shown in another method, females may excrete sex-related pheromones similar to the copepods ,  and rotifer  in order to increase successive mating with conspecies.
Several environmental factors can affect mating behavior by altering the encounter rate in Daphnia. Predator kairomones are the ultimate factor triggering predator avoidance responses as well as evoking behavioral and life history changes in prey . Male and female Daphnia select different distribution depths in the presence of fish kairomones , . Moreover, the presence of predator kairomones alters the swimming speed of Daphnia , and makes them sensitive to fluid disturbances, thereby enabling faster escape responses . These behavioral changes may influence the encounter rate or grasping for copulation in sexually reproducing Daphnia. Another candidate for alteration of the encounter rate is the food concentration. D. magna displays fast swimming with straightened tracks when ambient food is adequate . Food quantity regulates the distribution density in cladocerans such as D. pulex  and B. longispina ; they disperse when the food supply necessary for maintaining swarms is inadequate. Thus, food quantity may influence mating behavior through changes in the encounter rate. The fast swimming in males during mate searching resulted in an increase in the encounter rate with predators . Daphnia are preferred prey, and large females , especially sexual females with ephippium, are vulnerable to visual predators . Therefore, the rapid identification of receptive females (sexual females) among mixtures of both sexes is important to males, as well as sexual females.
Many researchers have focused on the initiation of sexual reproduction in Daphnia by environmental factors such as predation risk , food availability , and post–mating processes such as hatching of sexual eggs , . To the best of our knowledge, however, the interactive effects of environmental factors on the mating behavior of Daphnia have not yet been evaluated. In this study, we induced male and sexual female offspring from a clone of D. obtusa in the laboratory. We then observed mating behaviors of Daphnia and examined the effects of predation risk, food quantity, and females in different reproductive phases (asexual or sexual). The main objective of this study was to investigate the mating strategy of Daphnia according to environmental conditions. Particularly, we hypothesized that Daphnia males display reduced mating-related behaviors under predation risk and low food condition, and they show an ability to distinguish receptive females in the phase of sexual reproduction.
Materials and Methods
Field collections of Daphnia and fish in protected wetlands were carried out under the permission of the Ministry of Environment, and the field studies did not involve endangered or protected species. The Institutional Animal Care and Use Committee, which supervises animal experimentation at Sunchon National University, was not established when this study was conducted. Thus, our experiment was conducted without any type of committee approval. However, we maintained our experimental fish in a 560 L glass tank under room temperature with recirculation facility, and they were fed ad libitum with commercial frozen krill to comply with the animal protection laws of Korea. Fish was not sacrificed or released back to the Upo Wetlands and were maintained in the laboratory after the experiment.
D. obtusa is one of the most abundant species found in the Upo Wetlands in South Korea. They typically appear during spring and diminish after an extensive production of resting eggs in early summer. A clone used in mating experiments was isolated from the Upo Wetlands (35° 18' 8.58" N, 128° 41' 15.00" E), and maintained in an incubator at 20°C under a 12 h:12 h light–dark cycle. Basically, all cultures were kept in 500 mL transparent polycarbonate beakers containing Elendt M4 medium . Small green algae Chlorella vulgaris (strain number, UMACC 001) was added to the medium to achieve 2.5 mg·CL−1  during daily medium change.
Induction of male and sexual female Daphnia
10-day old D. obtusa females from culture were subjected to a high-density environment (200 individuals per 500 mL of medium) for male production. Neonates of the second clutch were collected. After 4–5 days, they were separated according to sex. Small, reddish, and fast-swimming males were maintained under a low-density regime (50 individuals per 500 mL of medium) until used. One half of the females was subjected to a high-density regime with no medium changes from day 9 in order to obtain sexual females with well-developed ovaries and immature white ephippium. The other half of females, which were kept under low-density conditions, was used as asexual females. During daily medium change, too small or large individuals due to variations in molting time were excluded. We used 12-day old sibling males as well as asexual and sexual females from the same clone for the mating experiment.
Factors for mating experiment
Fish kairomones were obtained from one large–mouth bass (Micropterus salmoides; total length c.15 cm), a species common in the Upo Wetlands. The fish was exposed to 10 L of Elendt M4 medium for 24 hours. Then, the medium was filtered through a 0.45 µm filter and stored at −20°C until used. Food concentrations were adjusted to low (0.5 mgCL−1) and high (2.5 mgCL−1) using C. vulgaris. Asexual or sexual females obtained from the culture were used in the experiment.
Observation of mating behavior
To evaluate the impact of predation risk (absence or presence of kairomones), food quantity (low or high), and reproductive phase of females (asexual or sexual) on mating, we conducted a 2×2×2 experimental design (12 replicates for each treatment, total of 96 observations). Small acryl chambers designed for two–dimensional observations were used (length × height × width = 8.5×7×0.5 cm). The observation chamber was placed in a box made of black panel without a cover or front side. All experiments were conducted during day time and a 20 W fluorescent lamp was placed above the box for illumination. We filled the observation chamber with 30 mL of medium for each treatment (absence or presence of fish kairomones and low or high food) and added 10 males and females (asexual or sexual). Before recording, there was an acclimation period of 10 minutes. We recorded all contact events for 10 minutes under each treatment using a digital camcorder (Sanyo Xacti VPC–SH1, Tokyo, Japan) recording at 30 frames per second. Contact frequency and frame number of the video for initiation and separation of every contact event were recorded (Fig. 1). Total frame numbers of each contact were used to calculate the duration time of contact. Simple collisions (when individuals swam in a different direction immediately without adherence) and contact events occurring before the recording or continued after 10 minutes were excluded.
Frame numbers of the video from encounter to separation of each contact were converted into time to determine the duration of the contact (black line: trajectory of male; grey line: trajectory of female; dashed line: trajectory of male and female during mating).
Mating and fighting in D. obtusa
Mating behavior in D. obtusa involved two types of contact; male–female contact (mating) and male–male contact (fighting). Males frequently changed their swimming direction toward individuals that passing nearby and chased the tracks of females or other males. Normally, mating behavior involved a strong escape response with fast swimming until the male became detached from the female. This reaction was also observed in fighting. Initially, males approached females from various directions, grasped a female with its modified hook-like first antennules, positioned itself on the ventral side, and attempted to insert its abdominal claw into the carapace valve of the female for insemination (Fig. 2).
Impact of predation risk
Fish kairomones had obvious and opposite impacts on the frequencies of both mating and fighting. In mating, the mean total contact frequency significantly (p = 0.004) increased from 12.9 to 16.4 in the presence of fish kairomones. On the other hand, the mean total contact frequency during fighting significantly (p = 0.000) decreased from 13.7 to 9.5 (Fig. 3A, B and Table S1) in the presence of fish kairomones. There was no statistical difference in duration time of mating between the control and fish kairomones treatments. Similarly, there was no effect of predation risk on the duration of fights. However, fights were distinctively shorter (0.7∼0.8 sec.) than male–female contact (Fig. 3C, D and Table S1).
Impact of food quantity
In terms of mating contacts, D. obtusa exhibited almost identical frequencies regardless of food quantity (14.8 at low food and 14.5 at high food) (Fig. 4A and Table S1). In contrast to the effect of fish kairomones, food quantity had a significant (p = 0.000) impact on the contact frequency of fighting; males tended to attach to other males more frequently when the ambient food concentration was high (9.6 under low food vs. 13.5 under high food conditions) (Fig. 4B and Table S1). Food quantity had no effect on the duration time. The duration of fighting was short, and both males separated quickly regardless of food quantity (Fig. 4C, D and Table S1).
Impact of reproductive phase of females
There was a significant (p = 0.000) increase in contact frequency according to the reproductive phase of females. In mating, the mean frequency was low (6.5) in male–asexual female combinations. However, there was a three–fold (22.7) increase when sexual females were put together with males. In addition, males contacted more frequently (p = 0.000) with other males when sexual females were present in the same observation chamber (Fig. 5A, B and Table S1). Despite this increase in frequency, the durations of mating and fighting were not dependent upon the sexual conditions of the females (Fig. 5C, D and Table S1).
During mating, the high visibility and unnatural swimming behaviors of males and sexual females make them vulnerable since size, transparency, and pigmentation of prey heavily affect predation rate , . The effects of predation on mating behavior have been tested for crustaceans such as decapod Rhynchocinetes typus, amphipod Gammarus duebeni, and copepod Cyclops vicinus. Male R. typus under predation risk from fish (Auchenionchus microcirrhis) did not change their mating behavior , whereas male and female G. duebeni show reduced activity leading to less pair formation in the presence of sticklebacks (Gasterosteus aculaetus) . C. vicinus exposed to Chaoborus kairomones show no decrease in mating, although both visual (roach; Rutilus rutilus) and tactile (phantom midge; Chaoborus flavicans) predators actually consumed more copepods during copulation . Thus, male–asexual female and male–sexual female contacts are undoubtedly risky in nature. Furthermore, fighting between males leads to predation risk.
In the presence of predation risk, Daphnia are subjected to a trade–off between mating and producing resting eggs for the next generation or avoiding mating in order to reduce mortality. When Daphnia perceives fish kairomones, they swim slowly to reduce the predatory encounter rate . Therefore, kairomones themselves may make encounters between the sexes more difficult. However, our results indicate an increase in mating frequency along with a decrease in fighting in the presence of fish kairomones. This suggests that Daphnia obviously take cues from predators and actively change their mating and fighting strategies according to the circumstances. Fast swimming during mating and fighting in Daphnia appear to be an escape behavior similar to the response against physical turbulence . Sexual reproduction is performed mainly during early summer, a time when predators are ubiquitous and this seasonal variation is hard to reverse until winter. Moreover, the switch to sexual reproduction occurs in response to population levels, and abundant sexual females exist even when there is a high predation risk. In this situation, investment in mating may be the best choice even under the worst conditions since the ultimate goal of both sexes is mating to ensure the transfer of genes.
It is well known that Daphnia recognize food concentrations and alter their behavior accordingly , . Moreover, recent molecular work has revealed that Daphnia have genes encoding gustatory receptors . Under low food conditions, Daphnia swim slowly possibly to save energetic costs , and as a result, low food can cause a low encounter rate. In this situation, males tend to avoid unnecessary fighting while mating is not affected. An established low food concentration or short periods of food stress in our experiment did not seem to affect mating, since Daphnia often experience low food conditions in the field .
In the experiment on the impact of reproductive phase of females, frequencies of male-sexual female contact were higher than those of male-asexual female and male-male contacts. Distinction of the receptiveness of females by males before actual contact is the most important factor in explaining this differential behavior. One feasible way for males to identify sexual females is chemical reception. Male copepods, such as Euryptemora affinis, E. herdmani, and Pseudodiaptomus coronatus are known to detected females or other males without actually making contact using pheromones operated within the genus level . Evidence for chemical interactions between males and females has also been found in the small cladoceran Chydorus sphaericus; males swim faster with complex tracks when females are present in the water . However, the use of water–soluble pheromones to assess the reproductive phase of females was not observed in the closely–related species D. pulicaria . Similarly, direct observation of the behavior of male D. magna to receptive sexual females did not support the presence of sex–related soluble chemicals . If D. obtusa indeed does not use chemicals for the distinction of sex and receptive female, other methods such as electrical or mechanical reception displayed by tactile predators can be used for mate selection . Daphnia make electrical noises when they swim . In addition, D. pulicaria and D. pulex produce detectable micro–turbulences larger than their body length when they swim , and these are affected by body size .
After contact, D. obtusa displayed significantly shorter and more consistent fighting duration compared to during mating regardless of conditions (Table S2). It is unclear whether or not such short interactions between males are enough to deter rivals and ensured possibility of mating. Previous studies on the mating behavior of the cladocerans D. pulicaria (average 13.8 sec. for mating and 1.6 sec. for fighting)  and M. brachiata (16∼25 sec. for mating and 1∼3 sec. for fighting)  have also confirmed short fighting durations. Therefore, it is suggested that males certainly distinguish the sexes of mates immediately after contact, and cues such as strength of escape behavior, size difference, and carapace morphology are considered. One of the most interesting aspects of the mating behavior of Daphnia is whether or not fruitless insemination occurs during male–asexual female contact. A precise insemination strategy according to the receptiveness of females following mate choice before contact can be predicted. Nevertheless, D. obtusa males showed insertion into the postabdomen to inseminate asexual D. obtusa females and even D. galeata females when pairs were carefully transferred and placed under the microscope for observation (Fig. 6). These observations suggest that the species and receptiveness of the female are not critical to copulation itself. This imprecision may be the cause of interspecific hybridization of cladocerans such as Bosmina , Daphnia  and Simocephalus .
Mating and fighting behaviors of D. obtusa can be summarized in three steps. 1. Pre–contact: the step of balancing. Factors such as predation risk, food quantity, as well as reproductive phase of females influence the chasing behavior of males. Males determine whether to chase or pass according to the magnitude of swimming turbulence. This enables the primary screening of other small males since adult females are normally larger than the male. 2. Contact: the step of sexing. The male distinguishes the sex of the contacted individual possibly based on differences in size and carapace shape. If the contacted individual is of the same sex, the male detaches immediately. 3. Post–contact: the step of actual copulation. In this step, external factors do not influence copulation and actual copulation is performed regardless of the species and receptiveness of the female. Mating in Daphnia does not occur randomly, but rather they assess multiple conditions before contact to maximize mating success. The results were expressed quantitatively (frequency) rather than qualitatively (duration), although the actual increase in the number of resting eggs according to enhanced mating requires further investigation.
Results of three–way ANOVA for the impact of three factors and their reciprocal interaction on the mating and fighting behavior of Daphnia obtusa.
Authors would like to thank Dr. Maria J. Gonzalez and two anonymous reviewers for the constructive comments to improve the manuscript.
Conceived and designed the experiments: GHL HWK. Performed the experiments: GHL JYC GJJ HWK. Analyzed the data: GHL KHC MHJ HWK. Contributed reagents/materials/analysis tools: GHL JYC HWK. Wrote the paper: GHL GJJ HWK.
- 1. Hebert PDN (1987) Genotypic characteristics of the Cladocera. Hydrobiologia 145: 183–193.
- 2. Pijanowska J, Stolpe G (1996) Summer diapause in Daphnia as a reaction to the presence of fish. J Plankton Res 18: 1407–1412.
- 3. Carvalho GR, Hughes RN (1983) The effect of food availability, female culture–density and photoperiod on ephippia production in Daphnia magna Straus (Crustacea: Cladocera). Freshwater Biol 13: 37–46.
- 4. Koch U, Von Elert E, Straile D (2009) Food quality triggers the reproductive mode in the cyclical parthenogen Daphnia (Cladocera). Oecologia 159: 317–324.
- 5. Fitzsimmons JM, Innes DJ (2006) Inter–genotype variation in reproductive response to crowding among Daphnia pulex. Hydrobiologia 568: 187–205.
- 6. Bernott RJ, Dodds WK (2006) Temperature and kairomone induced life history plasticity in coexisting Daphnia. Aquat Ecol 40: 361–372.
- 7. Deng HW (1997) Photoperiodic response of sexual reproduction in the Daphnia pulex group is reversed in two distinct habitats. Limnol Oceanogr 42: 609–611.
- 8. Hairston NG Jr, Kearns CM (2002) Temporal dispersal, ecological and evolutionary aspects of zooplankton egg banks and the role of sediment mixing. Integr Comp Biol 42: 481–491.
- 9. Innes DJ, Schwarz SSS, Hebert PDN (1986) Genotypic diversity and variation in mode of reproduction among populations in the Daphnia pulex group. Heredity 57: 345–355.
- 10. Jarnagin ST, Swan BK, Kerfoot WC (2000) Fish as vectors in the dispersal of Bythotrephes cederstroemi, diapausing eggs survive passage through guts. Freshwater Biol 43: 579–589.
- 11. Hairston NG Jr, Van Brunt RA, Kearns CM, Engstrom DR (1995) Age and survivorship of diapausing eggs in a sediment egg bank. Ecology 76: 1706–1700.
- 12. Wolf HG, Carvalho GR (1989) Resting eggs of lake–Daphnia II. In situ observations on the hatching of eggs and their contribution to population and community structure. Freshwater Biol 22: 471–478.
- 13. Tagg N, Innes DJ, Doncaster CP (2005) Outcomes of reciprocal invasions between genetically diverse and genetically uniform populations of Daphnia obtusa (Kurz). Oecologia 143: 527–536.
- 14. Forró L (1997) Mating behaviour in Moina brachiata (Jurine, 1820) (Crustacea, Anomopoda). Hydrobiologia 360: 153–159.
- 15. Gerritsen J, Strickler JR (1977) Encounter probabilities and community structure in zooplankton: a mathematical model. J Fish Res Board Can 34: 73–82.
- 16. Schwind R (1999) Daphnia pulex swims towards to the most strongly polarized light–a response that leads to ‘shore flight’. J Exp Biol 202: 3631–3635.
- 17. Young S (1974) Directional differences in the colour sensitivity of Daphnia magna. J Exp Biol 61: 261–267.
- 18. Larsson P (1991) Intraspecific variability in response to stimuli for male and ephippia formation in Daphnia pulex. Hydrobiologia 225: 281–290.
- 19. Innes DJ (1997) Sexual reproduction of Daphnia pulex in a temporary habitat. Oecologia 111: 53–60.
- 20. Spaak P, Denk A, Boersma M, Weider LJ (2004) Spatial and temporal patterns of sexual reproduction in a hybrid Daphnia species complex. J Plankton Res 26: 625–635.
- 21. Ratzlaff W (1974) Swarming in Moina affinis. Limnol Oceanogr 19: 993–995.
- 22. Young JPW (1978) Sexual swarms in Daphnia magna, a cyclic parthenogen. Freshwater Biol 8: 279–281.
- 23. Brewer MC (1998) Mating behaviours of Daphnia pulicaria, a cyclic parthenogen, comparisons with copepods. Philos T R Soc B 353: 805–815.
- 24. Kerfoot WC, Peterson C (1980) Predatory copepods and Bosmina: replacement cycles and further influences of predation upon prey reproduction. Ecology 61: 417–431.
- 25. Snell TW, Carmona MJ (1994) Surface glycoproteins in copepods: potential signals for mate recognition. Hydrobiologia 292/293: 255–264.
- 26. Lonsdale DJ, Frey MA, Snell TW (1998) The role of chemical signals in copepod reproduction. J Marine Syst 15: 1–12.
- 27. Rico–Martinez R, Snell TW (1995) Mating behavior and mate recognition pheromone blocking of male receptors in Brachionus plicatilis Müller (Rotifera). Hydrobiologia 313/314: 105–110.
- 28. Lass S, Spaak P (2003) Chemically induced anti–predator defences in plankton: a review. Hydrobiologia 491: 221–239.
- 29. Spaak P, Boersma M (2001) The influence of fish kairomones on the induction and vertical distribution of sexual individuals of the Daphnia galeata species complex. Hydrobiologia 442: 185–193.
- 30. Pijanowska J, Kowalczewski A (1997) Predator can induce swarming behaviour and locomotory responses in Daphnia. Freshwater Biol 37: 649–656.
- 31. Brewer MC, Dawidowicz P, Dodson SI (1999) Interactive effects of fish kairomone and light on Daphnia escape behavior. J Plankton Res 21: 1317–1335.
- 32. Young S, Getty C (1987) Visually guided feeding behaviour in the filter feeding cladoceran, Daphnia magna. Anim Behav 35: 541–548.
- 33. Larsson P (1997) Ideal free distribution in Daphnia? Are daphnids able to consider both the food patch quality and the position of competitors? Hydrobiologia 360: 143–152.
- 34. Jakobsen PJ, Johnsen GH (1988) The influence of food limitation on swarming behaviour in the waterflea Bosmina longispina. Anim Behav 36: 991–995.
- 35. Maly EJ (1970) The influence of predation on the adult sex ratio of two copepod species. Limnol Oceanogr 15: 566–573.
- 36. Brooks JL, Dodson SI (1965) Predation, body size, and composition of plankton. Science 150: 28–35.
- 37. Mellors WK (1975) Selective predation of ephippial Daphnia and the resistance of ephippial eggs to digestion. Ecology 56: 974–980.
- 38. Ślusarczyk M (1995) Predator–induced diapause in Daphnia,. Ecology 76: 1008–1013.
- 39. Ślusarczyk M (2001) Food threshold for diapause in Daphnia under the threat of fish predation. Ecology 82: 1089–1096.
- 40. Carvalho GR, Wolf HG (1989) Resting eggs of lake–Daphnia. I. Distribution, abundance and hatching of eggs collected from various depths in lake sediments. Freshwater Biol 22: 459–470.
- 41. Vandekerkhove J, Declerck S, Brendonck L, Conde–Porcuna JM, Jeppesen E, et al. (2005) Hatching of cladoceran resting eggs: temperature and photoperiod. Freshwater Biol 50: 96–104.
- 42. Elendt BP (1990) Selenium deficiency in Crustacea: an ultrastructural approach to antennal damage in Daphnia magna Straus. Protoplasma 154: 25–33.
- 43. Strathmann RR (1967) Estimating the organic carbon content of phytoplankton from cell volume or plasma volume. Limnol Oceanogr 12: 411–418.
- 44. Zaret TM (1969) Predation–balanced polymorphism of Ceriodaphnia cornuta Sars. Limnol Oceanogr 14: 301–303.
- 45. Kerfoot WC (1980) Commentary: transparency, body size and prey conspicuousness. In: Kerfoot WC, editor. Evolution and Ecology of Zooplankton Communities. pp.609–617.
- 46. Van Son TC, Thiel M (2006) Mating behavoiur of male rock shrimp, Rhynchocinetes typus (Decapoda: Caridea): effect of recent mating history and predation risk. Anim Behav 71: 61–70.
- 47. Dunn AM, Dick JTA, Hatcher MJ (2008) The less amorous Gammarus: predation risk affects mating decision in Gammarus duebeni (Amphipoda). Anim Behav 76: 1289–1295.
- 48. Maier G, Berger J, Burghard W, Nassal B (2000) Is mating of copepods associated with increased risk of predation? J Plankton Res 22: 1977–1987.
- 49. Brewer MC, Dawidowicz C, Dodson SI (1999) Interactive effects of fish kairomon and light on Daphnia escape behavior. J Plankton Res 21: 1317–1335.
- 50. Johnsen GH, Jakobsen PJ (1987) The effect of food limitation on vertical migration in Daphnia longispina. Limnol Oceanogr 32: 873–880.
- 51. Peñalva–Arana DC, Lynch M, Robertson HM (2009) The chemoreceptor genes of the waterflea Daphnia pulex: many Grs but no Ors. BMC Evol Biol 9: 79–89.
- 52. Luecke C, Vanni MJ, Magnuson JJ (1990) Seasonal regulation of Daphnia populations by planktivorous fish: implications for the spring clear–water phase. Limnol Oceanogr 35: 1718–1733.
- 53. Katona SK (1973) Evidence for sex pheromones in planktonic copepods. Limnol Oceanogr 18: 574–583.
- 54. Van Damme K, Dumont HJ (2006) Sex in a cyclical parthenogen: mating behaviour of Chydorus sphaericus (Crustacea; Branchiopoda; Anomopoda). Freshwater Biol 51: 2334–2346.
- 55. Winsor GL, Innes DJ (2002) Sexual reproduction in Daphnia pulex (Crustacea: Cladocera): observations on male mating behaviour and avoidance of inbreeding. Freshwater Biol 47: 441–450.
- 56. Crease TJ, Hebert PDN (1983) A test for the production of sexual pheromones by Daphnia magna (Crustacea: Cladocera). Freshwater Biol 13: 491–496.
- 57. Landry MR (1980) Detection of prey by Calanus pacificus: implications of the first antennae. Limnol Oceanogr 25: 545–549.
- 58. Freund JA, Schimansky–Geier L, Beisner B, Neiman A, Russell DF, et al. (2002) Behavioral stochastic resonance: how the noise from a Daphnia swarm enhances individual prey capture by juvenile paddlefish. J Theor Biol 214: 71–83.
- 59. Kirk KL (1985) Water flows produced by Daphnia and Diaptomus: implications for prey selection by mechanosensory predators. Limnol Oceanogr 30: 679–686.
- 60. Gries T, Jöhnk K, Fields D, Strickler JR (1999) Size and structure of ‘footprints’ produced by Daphnia: impact of animal size and density gradients. J Plankton Res 21: 509–523.
- 61. Lieder U (1956) Introgressive hybridization als evolutionsfaktor bei den gattungen Bosmina und Daphnia (Crustacea, Cladocera). Naturwissenschaften 43: 207.
- 62. Wolinska J, Löffler A, Spaak P (2007) Taxon–specific reaction norms to predator cues in a hybrid Daphnia complex. Freshwater Biol 52: 1198–1209.
- 63. Han BJ (1987) Naturally occurring interspecific hybridization in Simocephalus (Cladocera, Daphniidae): its potential significance. Hydrobiologia 145: 219–224.