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The effect of acceleration in light increase on the phototactic downward

swimming of Daphnia and the relevance to diel vertical migration.

van Gool, F.T.J.; Ringelberg, J.

DOI

10.1093/plankt/19.12.2041

Publication date

1997

Published in

Journal of plankton research

Link to publication

Citation for published version (APA):

van Gool, F. T. J., & Ringelberg, J. (1997). The effect of acceleration in light increase on the

phototactic downward swimming of Daphnia and the relevance to diel vertical migration.

Journal of plankton research, 19, 2041-2050. https://doi.org/10.1093/plankt/19.12.2041

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Journal of Plankton Research Vol.19 no.12 pp.2O41-2O5O, 1997

The effect of accelerations in light increase on the phototactic

downward swimming of Daphnia and the relevance to diel vertical

migration

Erik van Gool1'2 and Joop Ringelberg1-2

Centre for Limnology, Netherlands Institute of Ecology, Rijksstraatweg 6,3631 AC Nieuwersluis and 2 Department of Aquatic Ecology, University of Amsterdam,

The Netherlands

Abstract. The effect of relative increases in light intensity on photobehaviour was studied in the

hybrid Daphnia galeata x hyalina. We first carried out a series of experiments to study the influence of fish kairomone on several response variables of light-induced swimming. With fish kairomone present, an increase in the percentage of reacting daphnids to 100% was found at almost all ecologi-cally occurring relative light change rates that were above threshold. The relationship between the relative increase in light intensity (stimulus) and the time expiring between the onset of the stimulus and the start of the downward swimming response was not influenced by fish kairomone, nor did kairomone alter the functional relationship between stimulus strength and downward displacement velocity, although velocity increased. During the previous experiments, various light change rates were applied, but per test run these rates were constant The natural relative light increase in the early morning consists of continuously increasing relative light change rates, turning into decreasing rates after the maximum is reached -30-45 min before sunrise. In a second series of experiments, one step-increase in the rate of the relative light change was applied. We found that displacement velocity was higher than that expected if the second rate of increase had been given alone. Taking into account the newly found stimulus-acceleration effect, light-induced swimming might explain the amplitude of diel vertical migration found in lakes.

Introduction

The adaptive significance of diel vertical migration (predator avoidance; DVM) has been discussed in many recent papers, but causal explanations of the actual upward and downward movements at sunset and sunrise have received less atten-tion. Most experimental studies on DVM, whether performed in enclosures lowered in bays and lakes (Bollens and Frost, 1989; Neill, 1990), plankton towers (Loose, 1993; De Meester et al, 1995) or cylinders in the laboratory (Harris and Wolfe, 1956; Dawidowicz and Loose, 1992), are confined to descriptions of verti-cal distributions on a 24 h time sverti-cale. The behavioural mechanisms leading to these distributions are not studied. The interpretation of DVM in terms of adap-tive significance might be augmented if the underlying reaction mechanism is known, particularly what actually evokes downward and upward swimming in individuals. The functional hypothesis must be seen in the perspective of the stimuli that induce DVM because a behavioural mechanism must underlie adap-tivity.

Relative increases and decreases in light intensity have been used as definitions of the appropriate light stimulus that evokes downward and upward phototactic swimming responses, respectively. This phototaxis has been analysed in Daphnia magna (Clarke, 1932; Ringelberg, 1964; Daan and Ringelberg, 1967), D.longispina (Ringelberg, 1993) and D.galeata X hyalina (Ringelberg, 1991). A

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E.van Gool and J.Ringelberg

comparable phototaxis is also present in other species, for instance the marine calanoid Acartia tonsa (Stearns and Forward, 1987) and larvae of the crab Rhithropanopeus (Forward, 1985). It was shown in the laboratory that kairomones (infochemicals indicating predator presence) sensitize phototactic behaviour (Ringelberg, 1991; Forward and Hettler, 1992; De Meester, 1993; Loose etai, 1993; Van Gool and Ringelberg, 1995). Sensitization can be induced with water from the epilimnion, if sufficient fish biomass is present, whereas water from a fish-free hypolimnion has no such effect (Ringelberg, 1993). Hence, oriented swimming in response to relative changes in light intensity during sunrise and sunset, coupled to a perception of predator presence, was considered to be the behavioural mechanism underlying DVM. The vertical migration of Daphnia in Lake Maarsseveen (The Netherlands) is strongly correlated with relative light intensity changes at dawn and dusk (Ringelberg and Flik, 1994), which supports this hypothesis. Swimming is sustained as long as changes in light intensity exceed the phototactic response threshold, which is ~2 h at dawn. The swimming veloc-ities observed in the laboratory experiments were too low, however, to explain the sometimes large migration amplitudes (>10 m). Thus, the timing of vertical migration could be explained satisfactorily, but the amplitude not always (e.g. Ringelberg, 1995). To repair this shortcoming of the operative model, the effect of fish kairomone on the phototactic reaction of D.galeata X hyalina was studied again. The number of reacting animals in the presence and absence of fish kairomone at different stimulus strengths was determined, and the displacement velocities were measured. The results were thought to be insufficient to realize the desired extension of the potential migration amplitude. Next, it was hypo-thesized that a lowering of the stimulus threshold by kairomones would extend the period of morning descent and thus realize a larger migration depth. The stim-ulus strength-stimstim-ulus duration curve was determined, but the results refuted the hypothesis.

During these experiments, different relative light change rates were applied but, per test run, rates were kept constant. The natural light increase in the early morning might be described as continuously accelerating relative light change rates turning into decelerating rates after the maximum of the relative increase is reached -30-45 min before sunrise. We hypothesized that these accelerations might have an enhancing effect on swimming velocity. This proved to be the case and a first account of the results with accelerated rates in relative hght increases is presented in this paper.

Method

Individuals of a clone of the hybrid D.galeata X hyalina were used. The original female of this particular clone (stock culture M2) had been collected in the hypolimnion of Lake Maarsseveen (The Netherlands) at about noon during a period of DVM. The clone was cultured in the laboratory for almost 2 years before the experiments started. Stock cultures were grown in 1 1 bottles with water from the lake. This water had been circulated over a sand filter for several

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Increases in tight intensity and phototactk behaviour

days to remove possible traces of fish kairomones. Half of the water was refreshed every 2 weeks. Cultures were fed every other day with Scenedesmus acuminatus. A day-night cycle of 16:8 h light:dark was given, with light on at 6:00 h local time. Experiments were carried out between 11:00 and 14:00 h. Temperature was kept at 17 ± 0.5°C.

Experiments were performed in a vertically positioned perspex cylinder (diam-eter 10 cm, length 118 cm) placed in a perspex jacket with water from Lake Maarsseveen kept at the same temperature as in the cultures. This unit was placed inside a blackened, light-tight box. The cylinder was illuminated from above by three incandescent lamps (Philips, 25-60-25 W). A frosted perspex sheet was placed between the cylinder and the lamps to diffuse the light. Illumination inten-sity at the top of the cylinder was adjusted to the light inteninten-sity prevailing in Lake Maarsseveen (30 May 1990; Ringelberg et al., 1991) at the mean population depth of Daphnia (5.9 m) at sunrise (0.082 umol rcr2 s"1). Relative changes in light

inten-sity were accomplished with a variable resistance controlled by a computer. The algal {S.acuminatus) concentration in the cylinder was 0.5 mg I"1 C, which

is well above the incipient limiting level (ILL; above the ILL, ingestion rates remain constant) of 0.26 mg h1 C (determined for S.acutus; Muck and Lampert,

1984). This food concentration was re-established 1 h before a series of experi-ments started.

Water from a small aquarium (5 1) was continuously pumped into the cylinder. For experiments with the fish kairomone, the aquarium contained one juvenile perch {Percafluviatilis, 4 cm length). Water was fed back into the aquarium by an outflow at the bottom of the cylinder, screened by a gauze with a mesh size of 250 urn to keep daphnids inside. The pump rate was 7.8 ml min"1, which realized a

turnover in the cylinder of 1.5 times per 24 h. Circulation was started 1 day before the first light stimulus was applied. The physical absence of fish in the experi-mental cylinder ensured that only effects caused by the chemical presence of the kairomone were measured. Kairomone treatments and controls were studied on alternate observation days.

An infrared (IR)-sensitive video camera (Cohu Model 4110 Digital Video Monochrome CCD Camera, with a Schneider 1.4/17 mm Xenoplan lens), con-nected to a video recorder [Mitsubishi HS-E82(Y)] and a computer was used to observe the Daphnia in the cylinder. IR (kmax = 950 nm) illumination was used because ambient light intensity was too low to make the animals visible. Prelimi-nary experiments had revealed that there was no effect of this IR illumination on Daphnia behaviour.

During the experiments, consisting of different light intensity increases, all daphnids visible on the computer screen were followed. Afterwards, the position of individual animals was traced on the computer screen and the vertical position and time were registered by clicks of the cursor every 5 s.

Relative changes in light intensity (/) were calculated according to Ringelberg (1964) as:

^ - X ^ (1) 2043

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E.van Gool and J.Ringelberg

These stimuli for phototactic reactions are rates and are expressed as relative units per minute. Accelerations in rates were accomplished by increasing the initial rate stepwise after 2 min.

Important parameters of the phototactic reaction are the latent period and the vertical displacement velocity (dv). The first is defined as the time between the onset of the increase in light intensity and the start of the downward swimming reaction. This latency period was determined with an accuracy of 0.1 min. The displacement velocity is defined as a vertical distance covered by the responding animal, divided by the time needed to do this. The latency depends on the rate of the light increase and the relationship between both is characterized in the stimulus strength-stimulus duration curve. The rheobase (R) is an essential characteristic of this relationship and is defined as the value of the stimulus evoking a reaction when the duration is infinite. For a detailed description of the method of calculating R, see Ringelberg (1964, 1993). The value of R is deter-mined by iteration, using as criterion the best linear fit to the equation:

D I P

l X l ( 2 )

where Ip is the latency period measured at different stimulus strengths RLC and c is a rate constant.

Experiments were started by placing 60 adult D.galeata X hyalina females with eggs (first or second brood) from a culture in the experimental cylinder. These animals were used the next day only and then replaced by another set. Two kinds of experiments were carried out.

Experiment 1

Constant rates of relative light intensity increases were applied with values of 0.06, 0.08, 0.13,0.26,0.40 and 0.60 min"1. These light changes persisted for 15,12,

8, 5, 3 and 2.5 min, respectively. Each stimulus strength was repeated 4-6 times. Three different light increases were given to the same population of 60 animals. Tests were performed in the presence and absence of fish kairomone. This means that 16-24 sets of 60 Daphnia were used and as many days of experimentation. During a light increase period, all animals visible on the computer screen (5-12) were followed. Depending on stimulus strength, this resulted in a variable number (1-10) of observations of reacting animals.

Experiment 2

The effect of stimulus accelerations was studied by changing an initial relative light intensity increase (RLC1) after 2 min to a higher rate (RLC2). Within 2 min after the switch, the displacement velocity was measured for all 5-7 individuals visible on the computer screen. The average displacement velocity found in Experiment 1 [dV(RLCi)] was used to calculate the displacement velocity increase

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Increases in light intensity and phototactic behaviour

RCL1 (0.08 and 0.13 min"1) and RLC2 (0.15, 0.20, 0.25 and 0.30 mur1) were

tested, both in the presence and absence of fish kairomone. The small populations of 60 Daphnia were used in the same way as in Experiment 1 and thus 22-30 sets of 60 Daphnia were involved.

Of the 20—30 observations, comprising the presented averages, some might have been made on the same individual at a different light change. Therefore, it might be objected that pseudoreplication has biased these averages and no rep-resentation of the population is given. However, we deal with genetically identi-cal individuals and, theoretiidenti-cally, reactions of different individuals must be as variable as those of one individual at different stimuli. Other clones from the population of D.galeata X hyalina might be expected to behave differently. It was not our aim to present a population mean behaviour, but to demonstrate the basic causal mechanism of a particular behaviour.

Results Experiment 1

In the presence of kairomone, the percentage of Daphnia swimming downward in response to a single relative increase in light intensity increased rapidly as a function of stimulus strength (relative light increase rate); at a rate of change of 0.08 min-1, all animals reacted (Figure 1). In the absence of kairomone, 100%

reactions were not reached unless increases in light intensity were applied that do not occur in nature (i.e. >0.15 min"1, at 52.09°N, the geographical location of Lake

Maarsseveen).

Displacement velocity (dv) during the negatively phototactic swimming response is linearly related to stimulus strength (Figure 2). The slopes of the regression lines, with the stimulus as independent variable and average displace-ment velocity as dependent variable, obtained in the absence and the presence of

100

0.1 0.2 0.3 0.4 0.5 0.6

relative increase in Bght Intensity [min "']

0.7

Fig. L Mean percentage of responding Daphnia as a function of the relative increase in light

inten-sity. Error bars represent 95% confidence limits of the mean. Open dots represent the treatments without fish kairomone and closed dots represent the treatment with fish kairomone. The horizontal bar indicates the range of naturally occurring relative changes in light intensity.

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E-van Gool and JJUngelberg 25 n c 20-" 1

5-1

•a 0.0 0.1 0.2 0.3 0.4 0.5

relative increase in Bght Intensity [min"1 ]

0.6

Fig. 2. Vertical displacement velocity (dv) as a function of the relative increase in light intensity

(RLC). Without fish kairomone, open symbols, dv = 1.63 + 31.34 X RLC (R2 = 0.99, N = 6,P< 0.001);

with fish kairomone, closed symbols, dv = 2.71 + 30.74 x RLC (R2 = 0.99, N = 6, P < 0.001). Each

point in the figure represents the average of 20-35 individuals, except at the lowest rate (0.06 min-1)

when only a small proportion of the daphnids responded (N = 10) in the absence of kairomone. Error bars represent 95% confidence limits of the mean. Symbols are placed slightly next to each other on the horizontal axis to show the error bars more clearly.

fish kairomones were tested for equality (/-test; Zar, 1996) and found not to be different (f = 0.500, d.f. = 8; H^ pt = p2 is n o t rejected). Thus, the two lines are

assumed to be parallel and the nature of the causal relationship between stimu-lus strength and displacement velocity is not affected by kairomone. The differ-ence in elevation was significant (P < 0.01, t = 2.787, d.f. = 8; f-test; Zar, 1996). In the presence of fish kairomone, the displacement velocities were ~1 cm min"1

higher for the stimulus range tested.

Figure 3 shows the relationship between the relative increase in light intensity and the time expiring between the onset of this stimulus and the start of the down-ward swimming response (latency period). The best linear fit to equation (2) was obtained in the absence of kairomone and these data were used to calculate the rheobase value R = 0.04 mirr1 (R2 = 0.96, N = 6, P < 0.001). Kairomone seemed

not to influence the length of the latency period, and calculation of R in the absence and presence of kairomone led to the same rheobase value. Standard deviations of latency periods decrease with decreasing latency periods, i.e. increasing stimulus strengths (Figure 3): at low relative light change rates, some daphnids responded shortly after the onset of the light change, while others started downward swimming only after a few minutes.

Experiment 2

The influence of an acceleration in stimulus rate during a light intensity increase was very strong. As shown in Figure 4, a linear function relates the displacement velocity increase [^V(RLCI,RLC2)/^V(RLCI)] t o t n e ratio of both stimuli

(RLC2/RLC1). The resulting swiinming velocity far exceeded the value that goes with the second stimulus (RLC2), if given alone. Thus, an enlarged swimming 2046

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Increases in light intensity and photoUctic behaviour

1 ,

.1-.01

0 50 100 150 200 250 300 350 400 450 500

latency period [sec]

Fig. 3. The relationship between the relative increase in light intensity (RLC) and the latency period

(/p). Points represent means (N = 20-35) and 95% confidence limits of the mean latency period in the absence of kairomone are indicated. The line was drawn according to the equation In [RLC/(RLC -0.04)] = 4.6e-3 + 2.1e-3 x lp (R2 = 0.99, N = 6, P < 0.001), based on values from experiments in the

absence of kairomone (open dots). The closed dots represent the treatment with fish kairomone.

response follows upon acceleration of the rate of light intensity increase. Also plotted in Figure 4 is the relationship that would have been found if the acceler-ation had no effect on the displacement velocity, i.e. when dv measured after the RLC combination [dv(RLCi,RLC2)] were equal to the one to be found after

exposure to the second rate (RLC2) only. The latter relationship was found by calculating the ratio between dv(RLC2) and dv(RLC1), derived from experiments

with only one RLC per test run. The regression coefficients (slopes of the

4.5 4.0-3.0 « 2.5

M

3

2.0- 1.5-1.0 1.0 1.5 2.0 2.5 3.0 stimulus increase 3.5 4.0

Fig. 4. The relationship between the ratio of succeeding relative changes in light intensity

(RLC2/RLC1) and the increase in displacement velocity [dv(RU;i,RLC2/^V(RLCI)]- Each point

repre-sents the mean of 17-30 measurements performed with different daphmds. Error bars represent 95% confidence limits of the mean. The line is calculated for the observations in the absence of kairomone (open dots; y = -0395 + 1.408x, R2 = 0.972, N = 8,P< 0.001). The closed dots represent the treatment

with fish kairomone. The open triangles represent the values calculated as if stimulus acceleration has no effect (y = 0.663 + 0.516*, R2 = 0.923, P < 0.001).

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E.van Gool and J.Ringelberg

regression lines) of both relationships were significantly different (Mest; P < 0.001, t = 11.22, d.f. = 8).

In the presence of fish kairomone, the corresponding higher displacement velocities at the moment of the acceleration (Figure 2, closed dots) were enlarged by the same factor as found in the absence of kairomone (Figure 4). However, at very high acceleration values (RLC2/RLC1 > 3), behaviour became irregular, with several individuals doing somersaults. Downward swimming might even stop altogether when daphnids bumped into the wall of the cylinder. This aberrant behaviour is of no ecological consequence because it only appeared at unnatural high acceleration ratios. At two RLC2/RLC1 values (3.75 and 3.08), this inter-fered with the measurement of the displacement velocity to such an extent that these values (3.40 ± 0.40 and 2.89 ± 0.57, respectively) were not included in Figure 4.

Discussion

Phototaxis in Daphnia can be elicited by relative changes in light intensity alone; thus, in the absence offish kairomone. This holds especially for the higher stimu-lus values. Fish exudate increases the percentage of reacting animals, especially at those low stimulus values that approach the absolute threshold or rheobase. Our kind of analysis does not permit the recognition of individual daphnids at the different stimuli and we do not know whether the same individual always responded while others never did, or whether all individuals reacted, but discon-tinuously so. Qualitative observations support this latter interpretation, because even at ecologically high rates of light change it was sometimes observed that downward swimming stopped. The consequences for DVM are obvious: in the first case, a bimodal daytime vertical distribution will be found in a lake, while in the second case the distribution will be unimodal. During the migration period at Lake Maarsseveen, we never found bimodality (Ringelberg el ai, 1991; unpub-lished data).

The two parameters of the phototactic response mechanism, swimming veloc-ity (actually vertical displacement velocveloc-ity; Figure 2) and stimulus thresholds (Figure 3), were not affected much by the presence of fish kairomone. Swimming velocity also depends on animal size and differently sized Daphnia species cannot be compared. Stimulus thresholds, however, can, and the relationship between stimulus strength and the latency period in D.galeata X hyalina differs little from that found in D.magna (Ringelberg, 1964) or D.longispina (Ringelberg, 1993). Absolute thresholds or rheobase values are 0.04, 0.10 and 0.055 min"1,

respec-tively. If present, these differences may also result from different adaptation light intensities. In the present study, this light intensity was very low compared to that in both previous studies. The influence of adaptation light intensity on thresholds in continuous light changes is unknown, but for instantaneous decreases Ringel-berg et al. (1967) found the threshold (i.e. just noticeable difference) to increase with increasing light intensity.

Relative changes in light intensity do not represent a complete stimulus for phototaxis, and thus not for DVM. Two successive relative changes of different 2048

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Increases in light intensity and phototactic behaviour

magnitude do not act independently. A second relative change of higher magnitude provides an acceleration moment that sets a new pace for swimming velocity. Actually, the vertical displacement velocity belonging to the second rela-tive change [rfv(RLC2)], when this would have been the first and only one, is

mul-tiplied by a factor. This factor, given by the slope of the linear relationship of Figure 4, is constant and independent of the ratio between the first and the second stimulus. As with the displacement velocity (Figure 2) and the threshold of the stimulus strength-stimulus duration curve (Figure 3), the presence of a fish kairomone does not affect the value of the enhancing effect. Therefore, the accel-eration phenomenon must be considered part of the phototactic response mechanism and, as such, is an extension to the mechanistic model that has been presented by Ringelberg (1995).

Experimentally determined values of phototactic response parameters may be used to calculate an early morning descent as occurring in a lake. Starting at early dawn, the natural light signal as measured, for instance, below the water surface of Lake Maarsseveen (June 1992) can be thought to consist of gradually increas-ing relative increases in light intensity. The resultincreas-ing acceleration is about con-stant until the maximum of the relative light change rate is reached at -30-45 min before sunrise. Then a deceleration of the relative light change rate sets in, although light intensity is still increasing. Various aspects of this acceleration-assisted stimulus response system, including the effect of these decelerations, are the subject of continued experimentation. However, preliminary simulation of downward migration in response to a light change at sunrise, taking into account the newly found stimulus acceleration effect, and thus increased displacement velocity, proved easily to realize the large amplitudes (>10 m) of DVM sometimes found in Lake Maarsseveen.

Acknowledgements

We would like to thank Maurice Sabelis and three anonymous reviewers for their comments on an earlier version of this manuscript, and Luc De Meester for fruit-ful discussions. This study was supported by the Life Science Foundation (SLW), which reports under the Netherlands Organization of Scientific Research (NWO).

References

Bollens,S.M. and Frost.B.W. (1989) Predator-induced diel vertical migration in a planktonic copepod. /. Plankton Res., 11,1047-1065.

Clarke.G.L. (1932) Quantitative aspects of the change of photopic sign in Daphnia. J. Exp. Biol., 9, 180-211.

Daan,N. and RingelbergJ. (1967) Further studies on the positive and negative phototactic reaction of Daphnia magna Straus. Neth. J. Zooi, 19, 525-540.

Dawidowicz,P. and Loose.C J. (1992) Metabolic costs during predator induced diel vertical migration of Daphnia. LimnoL Oceanogr., 37, 1589-1595.

De Meester^L. (1993) Genotype, fish mediated chemicals and phototactic behaviour in Daphnia

magna. Ecology, 74,1467-1474.

De MeesterJ^, Weider,LJ. and Tollrian^R. (1995) Alternative antipredator defences and genetic polymorphism in a pelagic predator-prey system. Nature, 378,483-485.

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E.van GooJ and J.Ringelberg

Forward.R.B.Jr (1985) Behavioural responses of larvae of the crab Rhithropanopeus harrisii (Brachyura: Xanthidae) during diel vertical migration. Mar. Bwl., 83, 9-18.

Forward.R.B.Jr and Hettler.W.FJ.Jr (1992) Effects of feeding and predator exposure on photo-responses during diel vertical migration of brine shrimp larvae. Limnol. Oceanogr., 37,1261-1270. Harris J.E. and Wolfe,U.K. (1956) A laboratory study of vertical migration. Proc. R. Soc London Sen

B, 144, 329-355.

Loose,C.J. (1993) Daphnia diel vertical migration behaviour Response to vertebrate predator abundance. Ergebn, Limnol., 39, 29-36.

MuckJ". and Lampert.W. (1984) An experimental study on the importance of food conditions for the relative abundance of calanoid copepods and cladocerans. Arch. Hydrobioi, 66(SuppL), 157-179. Neill.W.E. (1990) Induced vertical migration in copepods as a defence against invertebrate predation.

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RingelbergJ. (1964) The positively phototactic reaction of Daphnia magna Straus: A contribution to the understanding of diurnal vertical migration. Neth, J. Sea Res., 2, 841-847.

RingelbergJ. (1991) Enhancement of the phototactic reaction in Daphnia hyalina by a chemical mediated by juvenile perch (Perca fluviatilis). J. Plankton Res., 13, 17-25.

RingelbergJ. (1993) Phototaxis as a behavioural component of diel vertical migration in a pelagic

Daphnia. Ergebn, Limnol., 39, 45-55.

RingelbergJ. (1995) An account of a preliminary mechanistic model of swimming behaviour in

Daphnia: its use in understanding diel vertical migration. Hydrobiologia, 307,161-165.

RingelbergJ. and Flik,B-JG. (1994) Increased phototaxis in the field leads to enhanced diel vertical migration. Limnol. Oceanogr., 39, 1855-1864.

RingelbergJ., Flik,B.J.G., Lindenaar.D. and RoyackersJC. (1991) Diel vertical migration of Daphnia

hyalina (sensu latiori) in Lake Maarsseveen: Part 1. Aspects of seasonal and daily timing. Arch. Hydrobioi., 121, 129-145.

RingelbergJ., Van KasteelJ. and Servaasji. (1967) The sensitivity of Daphnia magna Straus to changes in light intensity at various adaptation levels and its implication in diurnal vertical migration. Z. Vgl. PhysioL, 56, 397^107.

Stearns.D.E. and Forward,R.B.,Jr (1984) Photosensitivity of the calanoid copepod Acartia tonsa. Mar.

Bioi, 82, 85-89.

Van Gool,E- and RingelbergJ. (1995) Swimming of Daphnia galeata x hyalina in response to changing light intensities: Influence of food availability and predator kairomone. Mar. Freshwater

Behav. PhysioL, 26, 259-265.

ZarJ. (1996) Biostatistical Analysis, 3rd edn. Prentice Hall, Upper Saddle River, NJ.

Received on June 4, 1996; accepted on August 20, 1997

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