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738 J. Phycol. 37, 738–743 (2001) GRAZING AND GROWTH OF THE MIXOTROPHIC CHRYSOMONAD POTERIOOCHROMONAS MALHAMENSIS (CHRYSOPHYCEAE) FEEDING ON ALGAE 1 Xiaoming Zhang 2 and Makoto M. Watanabe National Institute for Environmental Studies, 16-2 Onogawa, Tsukuba, Ibaraki 305-0053, Japan The growth and grazing characteristics of Poterioo- chromonas malhamensis (Pringsheim) Peterfi ( � Ochromo- nas malhamensis Pringsheim) (ca. 8 � m) feeding on phy- toplankton, including the cyanobacteria Synechococcus sp. (ca. 2 � m) and Microcystis viridis (A. Brown) Lemmer- mann (ca. 6 � m) and the green alga Chlorella pyrenoi- dosa Chick (ca. 13 � m), were investigated in laboratory experiments involving the following treatments: (1) light without added algal prey (autotrophy), (2) light with added algal prey (mixotrophy), and (3) dark with added algal prey (phagotrophy). There were sig- nificantly higher cell numbers under mixotrophic and phagotrophic growth than under autotrophic growth. With phytoplankton as food, growth rates under both mixotrophy and phagotrophy were about two or three times higher than those under autotrophy, indicating that the algal diets were readily able to support the population growth of P. malhamensis. There were no significant differences in growth rate between mix- otrophic and phagotrophic cultures during exponen- tial growth. The ingestion rate of P. malhamensis with algal prey was also similar under both continuous light and dark. Poterioochromonas malhamensis ingested on average 0.27 M. viridis cells � flagellate � 1 � h � 1 and 0.18 C. pyrenoidosa cells � flagellate � 1 � h � 1 in continuous light and 0.25 M. viridis cells � flagellate � 1 � h � 1 and 0.18 C. pyrenoidosa cells � flagellate � 1 � h � 1 in continuous dark during exponential growth. The results showed that light had no effect on the growth and ingestion rates of P. malhamensis for phagotrophy during exponential growth. However, phagotrophic populations of P. mal- hamensis were incapable of growth in continuous dark- ness for longer than 5 days. Populations of P. malha- mensis showed no increase when prey was added again after 4 days in continuous darkness, indicating that light is necessary for sustained phagotrophic growth of P. malhamensis. The study suggests that P. malhamensis , which has strong tolerance for light, is light dependent for phagotrophy. Key index words: Chrysomonad; growth rate; herbivo- rous grazer; ingestion rate; mixotrophy; phagotrophy Mixotrophic chrysomonads, which are capable of both photosynthesis and phagotrophy, are now recog- nized to play an important role in grazing bacteria and in regenerating nutrients within marine and freshwa- ter planktonic ecosystems (e.g. Estep et al. 1986, Bird and Kalff 1986, 1987, 1989, Boraas et al. 1988, Porter 1988, Salonen and Jokinen 1988, Andersson et al. 1989, Sanders et al. 1989, 1990, Sanders 1991, Bennett et al. 1990, McKenzie et al. 1995). Previous laboratory experiments suggested that bacterivory by mixotro- phic chrysomonads seems to be the dominant mode of nutrition in all cultures containing heat-killed bac- teria (Andersson et al. 1989, Caron et al. 1990, Sanders et al. 1990). Many field studies have also shown the im- pact of mixotrophic chrysomonads on bacterioplank- ton in oceans and fresh waters and support the hypoth- esis that mixotrophic chrysomonads can control the abundance and growth of bacteria (Bird and Kalff 1986, 1987, Sanders and Porter 1988, Sanders et al. 1989, McKenzie et al. 1995). Therefore, mixotrophic chrysomonads are generally considered an important group of bacterivores in some marine and freshwater planktonic ecosystems. Nevertheless, it has also been shown that mixotrophic chrysomonads such as Ochromo- nas , Poterioochromonas , and Chrysamoeba also feed on vari- ous algae and bacteria (Pringsheim 1952, Daley et al. 1973, Cole and Wynne 1974, Boraas et al. 1988, Zhang et al. 1996, Holen 1999), so mixotrophic chrysomonads are not just functional bacterivores. Despite previous studies showing the importance of assessing the impact of grazing on various algae by these pigmented chry- somonads, very little attention has been given to the eco- logical role of mixotrophic chrysomonads as herbivores. There is a clear need to examine the growth and inges- tion rates of these mixotrophic chrysomonads when sup- plied with phytoplankton prey. It has been reported that Poterioochromonas malha- mensis , a well-known bacterivorous chrysomonad, de- rives only 7% of its total carbon budget from photo- synthesis, the remainder being obtained from bacteria (Sanders et al. 1990). This alga has been demonstrated to digest and assimilate carbon and nutrients from bac- teria with efficiencies similar to truly heterotrophic nanoflagellates (Caron et al. 1990). In a previous study, we examined in detail a range of prey grazed by P. mal- hamensis (Zhang et al. 1996). The results indicated that P. malhamensis is capable of ingesting various kinds of organisms, ranging from pico-, nano-, and microplank- ton to motile algae, including the cyanobacteria Synecho- coccus and Microcystis , the diatom Achnanthes , the chry- somonad Uroglena , and the green algae Chlorella and Carteria. Our study demonstrated for the first time that P. malhamensis is capable of grazing algae two to three times larger than its own cell diameter and increasing in size by 10–30 times that of a normal cell. Thin sec- 1 Received 30 August 2000. Accepted 6 June 2001. 2 Author for correspondence: e-mail Zhang.xiaoming@nies.go.jp. GRAZING AND GROWTH OF P. MALHAMENSIS 739 tions examined by TEM showed that P. malhamensis was not only ingesting but also digesting the prey Syn- echococcus , Microcystis , Chlorella , and Chlamydomonas (Zhang et al. 1996). These studies therefore suggested that P. mal- hamensis may be an important grazer not only of bacteria but also of pico-, nano-, and microphytoplankton. Despite the potential importance of its effect on phytoplankton, it remains uncertain whether P. malhamensis can use such phytoplankton to support its population growth. Here we present further work that compares the in- gestion and growth rates of P. malhamensis feeding on al- gae during the day and night. We selected three species of alga differing in size, shape, and taxonomy, the cy- anobacteria Synechococcus sp. (2 � m) and Microcystis viri- dis (ca. 6 � m) and the green alga Chlorella pyrenoidosa (ca. 13 � m), for grazing experiments. Our results confirm that not only bacteria but also phytoplankton algae could support the population growth of P. malhamensis. materials and methods Algal culture. The culture strain of P. malhamensis (ca. 8 � m diameter, 268 � m 3 volume) was from the chrysomonad collec- tion of the first author (X. Z.) and is maintained at the Microbial Culture Collection, National Institute for Environment Studies, Japan Environment Agency. Cultures were grown in 2-L Erlen- meyer flasks with 1 L modified AF-6 medium (Kato 1982) under il- lumination of ca. 100 � mol photons � m � 2 � s � 1 with a photoperiod of 12:12-h light:dark from daylight fluorescent lamps at 20 � C. Preparation of prey algae. Cultures of thecyanobacteria Syn- echococcus sp. (axenic, clonal, PS-717) and M. viridis (axenic, clonal, NIES-102) and the chlorophyte C. pyrenoidosa (axenic, clonal, NIES-226), used as prey organisms, were obtained from the Microbial Culture Collection, National Institute for Environ- ment Studies, Japan Environment Agency. The algal strains were grown in 200-mL Erlenmeyer flasks with 100 mL of growth me- dium suited for each algal culture (Watanabe and Nozaki 1994). Each algal species was grown to a moderately dense culture, har- vested by centrifugation, and heat killed at 70 � C for 30 min. Experimental treatments. The responses of growth and inges- tion rates to prey availability were determined for each prey— Synechococcus sp, M. viridis , and C. pyrenoidosa —or a mixture of 25% of each of them and a bacterium. The final concentration of prey was adjusted to 6 � 10 6 cells � mL � 1 . For the feeding ex- periments, P. malhamensis cells in exponentially growing popu- lations were harvested and washed three times with sterile me- dium. The prey algae were added to P. malhamensis cultures and incubated for 10 days. Experiments with prey were divided into two parts, with or without light. Cultures with prey incu- bated in continuous light were under illumination of ca. 100 � mol photons � m � 2 � s � 1 . Cultures with prey incubated in contin- uous dark were wrapped in foil and sampled in almost total darkness. Control cultures in the light without prey were incu- bated in parallel with other cultures. All experimental treat- ments were performed in three replicate cultures. The growth temperature for all cultures used was 20 � C. Samples were ob- served daily, and all samples for cell counts were preserved with buffered glutaraldehyde (1% final concentration). Determination of growth rate. Cell counts from triplicate sam- ples were determined using hemacytometer chambers through- out the growth cycle of the population. Samples for prey and algal cell counts were taken aseptically at t � 0 and at about 24-h inter- vals up to day 8 in each experimental treatment. Specific growth rates of P. malhamensis, �(d�1), in the various treatments were de- termined from regressions of the linear portion of the growth curves expressed as the natural log of the population density ver- sus time (i.e. exponential growth phase). The specific growth rate of P. malhamensis, �(d�1), was calculated as �(d�1) � (lnPt � lnP0)/t, where P0 is the initial concentration of P. malhamensis and Pt is the final concentration of P. malhamensis (cells�mL�1) after time t (d). Ingestion rate. Ingestion rates of algae by P. malhamensis were calculated using the equations of Heinbokel (1978). Ingestion rates were determined by the disappearance of prey in the cul- tures using the following formula: Ic � �P/F�t � �P/[(F2 � F1) (lnF2 � lnF1) � �t], in which �P is the decrease in prey cell number during time interval �t and F2 and F1 are the pred- ator cell densities (cells�mL�1) at the end and beginning, re- spectively, of each interval (Heinbokel 1978). Although bacteria may have been present in the experimen- tal cultures, the collected P. malhamensis cells were washed three times with sterile medium to decrease bacterial numbers before the experiments. Therefore, ingestion and growth rates were analyzed only in relation to prey algal density. results Growth rates. Populations of P. malhamensis fed on M. viridis exhibited a 1-day lag phase followed by expo- nential growth for incubation periods as long as 3 days under continuous light or dark (Fig. 1, A and B). Dur- ing exponential growth, there was not a significant dif- ference in growth rate between cells grown with M. vir- idis as prey under continuous light and dark (Fig. 1, A and B, Table 1; Student’s t-test, P 0.05). In the con- trol experiment, cell numbers of P. malhamensis in- creased slowly (Fig. 1C). However, the cell numbers of P. malhamensis for phagotrophy in cultures placed in continuous dark using M. viridis as prey increased up to day 4 after inoculation. Then, the cell densities of P. malhamensis decreased gradually after day 4, whereas M. viridis prey cells increased slightly in the cultures (Fig. 1B). The same pattern was observed for P. malha- mensis ingestion of C. pyrenoidosa, except that the pop- ulation of P. malhamensis showed constant exponen- tial growth for 4 days without a lag phase under both light and dark (Fig. 2, A and B). There was no signifi- cant difference in growth rate between cells grown with C. pyrenoidosa as prey under continuous light and dark (Table 1; t-test, P 0.05). There were major con- trasts in the patterns of growth in the two grazing ex- periments with or without light, which coincided with the end of exponential growth of P. malhamensis in both mixotrophic and phagotrophic experiments. In mixotrophic experiments, there was a continuous in- crease in the cell numbers of P. malhamensis after the end of exponential growth. Populations of P. malha- mensis fed on M. viridis or C. pyrenoidosa exhibited sta- tionary phase growth by day 4 in continuous light (Figs. 1A and 2A). In phagotrophic experiments, the cell numbers of P. malhamensis decreased gradually af- ter the end of exponential growth, and no stationary phase growth was observed (Figs. 1B and 2B). The cell yields grown with the same prey were significantly higher in all light treatments (mixotrophy) than in all dark ones (phagotrophy) (Table 1; t-test, P � 0.05). There were higher rates of increased cell numbers under phagotrophic or mixotrophic growth than un- der autotrophic growth. With both M. viridis and C. pyrenoidosa as food prey, growth rates in the light or dark were about two or three times higher than those without added food prey (autotrophic) (Figs. 1 and 2, 740 XIAOMING ZHANG AND MAKOTO M. WATANABE Fig. 1. Growth of Poterioochromonas malhamensis (�, �) feeding on Microcystis viridis at a prey concentration of 6 � 106 cells�mL�1 and changes in cell density of prey (�, �) as a func- tion of incubation time under continuous light (A) or continu- ous dark (B). A control experiment (C) under continuous light showing autotrophic growth of P. malhamensis (�). Vertical bars show SD (n � 9, based on three replicate cultures). Table 1). The growth rates between autotrophic growth and phagotrophic or mixotrophic growth were significantly different in all treatments (Table 1; t-test, P � 0.05). Addition of prey had a significant ef- fect on growth rate (analysis of variance [ANOVA], F � 109, P � 0.0001). For the mixotrophic (light with prey) experiment, the growth rate (d�1) of P. malha- mensis was 0.71 for Synechococcus sp. as food and 0.85 with M. viridis, 0.75 for C. pyrenoidosa, and 0.89 when a mixture of bacteria, Synechococcus sp., M. viridis, and C. pyrenoidosa was added as food (Table 1). For the phag- otrophic (dark with prey) experiments, the growth rate (d�1) was 0.81 with Synechococcus sp. as food, 0.90 with M. viridis, 0.79 with C. pyrenoidosa, and 0.82 for a mixture of bacteria, Synechococcus sp., M. viridis, and C. pyrenoidosa as food (Table 1). There was no significant difference in growth rate between mixotrophy and phagotrophy with the same prey for all treatments (t -test, P 0.05); also no significant difference was seen in growth rate between mixotrophy and phag- otrophy with different prey (P 0.05). Light or dark had no significant effect on growth rate (ANOVA, F � 1.715, P � 0.209). The effect of light and prey density was studied in an experiment where M. viridis was added again to P. Fig. 2. Growth of Poterioochromonas malhamensis (�, �) feeding on Chlorella pyrenoidosa at a prey concentration of 6 � 106 cells�mL�1 and changes in cell density of prey ( , ) as a function of incubation time under continuous light (A) or con- tinuousdark (B). Vertical bars show SD (n � 9, based on three replicate cultures). A control experiment (C) under continu- ous light showing autotrophic growth of P. malhamensis (�). GRAZING AND GROWTH OF P. MALHAMENSIS 741 malhamensis cultured in continuous dark with M. viri- dis. A population of M. viridis as high as 9.8 � 106 cells�mL�1 was added to cultures of P. malhamensis. The original dark sample was split into two cultures on day 4 after adding the prey. One culture was main- tained in the dark and the other transferred to the light (Fig. 3). After 24 h, there was an obvious in- crease in P. malhamensis cell density in the light and a decrease in the dark (Fig. 3). The cell numbers in the light treatment were significantly higher than in the dark when tested using a two-sample t-test for adding prey at 24 h and 48 h (P � 0.05, Table 2). Ingestion rate. The maximum ingestion rate occurred during the first sampling interval during which the prey density decreased precipitously. When M. viridis was used as food prey, ingestion rates were 3.2 cells� flagellate�1�h�1 in the light and 3.9 cells�flagellate�1�h�1 in the dark (Ta- ble 3). The maximum ingestion rate was not significantly different between the light and dark conditions with M. viridis as prey (t-test, P 0.05). When C. pyrenoi- dosa was used as food prey, the ingestion rate was 1.8 cells�flagellate�1�h�1 in the light and 1.2 cells� flagellate�1�h�1 in the dark (Table 3). There was not a significant difference in maximum ingestion rate be- tween the light and dark treatments when C. pyrenoi- dosa was used as prey (P 0.05). However, prey type had a significant effect on maximum ingestion rates (ANOVA, F � 33.8, P � 0.0002). During exponential growth, the average ingestion rate of P. malhamensis for M. viridis was 0.27 cells� flagellate�1�h�1 in continuous light and 0.25 cells� flagellate�1�h�1 in continuous dark (Table 3). On the other hand, the average ingestion rate of P. malhamen- sis for C. pyrenoidosa was 0.18 cells�flagellate�1�h�1 in continuous light and 0.18 cells�flagellate�1�h�1 in the dark. There was not a significant difference in average ingestion rate between the light and dark treatments when M. viridis or C. pyrenoidosa was used as prey (P 0.05). However, prey type had a significant effect on ingestion rates (ANOVA, F � 34.9, P � 0.0001). discussion Little direct experimental evidence of mixotrophic chrysomonads growing on algae has been documented until now (Holen 1999). Although Cole and Wynne (1974) also showed that mixotrophic Ochromonas danica Prings is capable of grazing the toxic cyanobacterium Table 1. Growth parameters for Poterioochromonas malhamensis cultured under autotrophic, mixotrophic, and phagotrophic conditions. Prey Size (�m) Treatment Growth rate �(d�1) Cell yield (cells�mL�1) Synechococcus sp. 2.0 Light 0.71 � 0.04a 3.76 � 105 � 0.13a Dark 0.81 � 0.087a 1.01 � 105 � 0.13b Microcystis viridis 5.6 Light 0.85 � 0.097a 8.45 � 105 � 1.03a Dark 0.90 � 0.058a 4.27 � 105 � 0.45b Chlorella pyrenoidosa 13.3 Light 0.75 � 0.04a 1.29 � 106 � 0.16a Dark 0.79 � 0.03a 4.86 � 105 � 0.56b B S. M. C. Light 0.89 � 0.04a 9.90 � 105 � 0.30a Dark 0.82 � 0.04a 2.41 � 105 � 0.29b Autotrophy Light 0.32 � 0.031b Means � SD (n � 3, based on three replicate cultures) are not significantly different in growth rate between the light and dark treatments with the same prey (common letters) (P 0.05), not significantly different between the light and dark treatments with different prey (P 0.05), but significantly different between autotrophy and mixotrophy or phagotrophy (different letters) (P � 0.05). Cell yield was calculated as the maximum algal density minus the initial density. Means � SD (n � 3, based on three replicate cultures) are significantly different between the light and dark treatments with the same prey (different letters) (P � 0.05). B, bacteria; C, Chlorella pyrenoidosa; M, Microcystis viridis; S, Synechococcus sp. Fig. 3. Effect of light and prey on growth of Poterioochromo- nas malhamensis. Poterioochromonas malhamensis was fed Microcys- tis viridis at an initial concentration of 5.6 � 106 cells�mL�1 and incubated in continuous dark. After 4 days, the dark-treated cultures received M. viridis as prey again at an initial concentra- tion of 9.8 � 106 cells�mL�1 and split into two parts (arrow), one of which was maintained in continuous dark (�) and the other incubated in continuous light (�). Vertical bars show SD (n � 8–12, based on three replicate cultures). Table 2. Poterioochromonas malhamensis comparison of cell numbers after adding Microcystis viridis as prey. Time Treatment Cell numbers (�105�mL�1) 24 h Light 5.38 � 0.68 Dark 3.48 � 0.57 48 h Light 11.57 � 1.01 Dark 2.87 � 0.31 Means � SD (n � 8, based on three replicate cultures) are significantly different between the light and dark treatments (P � 0.05). 742 XIAOMING ZHANG AND MAKOTO M. WATANABE Microcystis aeruginosa, the grazing and growth rates of O. danica on M. aeruginosa were not given. The present study is apparently the first to provide data on both graz- ing and growth rates of a mixotrophic chrysomonad feed- ing on algae. Our results indicate that the mixotrophic P. malhamensis is capable of ingesting three kinds of algae to support its growth. The grazing and growth charac- teristics of P. malhamensis indicate that it is well suited for existence in phytoplankton communities. When feeding on algae, P. malhamensis showed growth rates for both mixotrophy and phagotrophy two to three times higher than those for autotrophy, indicating that the algal diets were readily able to support the population growth of P. malhamensis. However, the growth rates of herbivorous P. malhamensis were lower in this study (0.71–0.90 d�1) than in earlier ones (1.5– 2.2 d�1), when bacteria as prey were not limited (Sanders et al. 1990, Caron et al. 1990). There are two possible explanations for this difference. First, the prey density in our study may have been below the sat- urating concentrations for sustaining the maximum specific growth rates of P. malhamensis. Sanders et al. (1990) also pointed out that prey density was the pri- mary factor influencing the ingestion and growth rates of P. malhamensis. Second, different strains of the same species collected from different places may have different growth rates, as we observed in two strains of P. malhamensis showing different growth rates (unpub- lished data). The maximum ingestion rates (about 1.2–3.9 cells� flagellate�1�h�1) calculated for P. malhamensis in this study were lower than rates (about 89–103 bacte- ria�flagellate�1�h�1) previously determined for the same species feeding on bacteria (Sanders et al. 1990, Caron et al. 1990). The lower rates can be explained by the considerably larger cell size (6–13 �m) of the prey used in our study. For example, when M. viridis (ca. 6 �m) was used as food, 3.9 cells�flagellate�1�h�1 in the light and 3.2 cells�flagellate�1�h�1 in the dark were de- termined, whereas only 1.8 cells�flagellate�1�h�1 in the light and 1.2 cells�flagellate�1�h�1 in the dark were mea- sured when the larger sized C. pyrenoidosa (ca. 13 �m) was used as food. Our results indicate that prey type had a significant effect on maximum ingestion rates (ANOVA, F � 33.8, P � 0.0002). Mixotrophy is commonly found among chrysomonads and other nanoplankton (Bird and Kalff 1986, Sanders et al. 1989, 2000, Sanders 1991). Mixotrophic chrysomonads such as Ochromonas, Dinobryon, and Uroglena can occur at very high densities in natural environments (Kimura and Ishida 1985, 1986, Bird and Kalff 1986, Sanders et al. 1989, Olrik and Nauwerck 1993). Previous studies have reported that mixotrophic Ochromonas is capable of grazing cyanobacteria (Anacystis and Microcystis) and a green alga (Daley et al. 1973, Cole and Wynne 1974, Boraas et al. 1988). Ochromonas sp. was found to signif- icantly reduce a bloom of small unicellular centric di- atoms in Hjarbak Fjord Lake, Denmark (Olrik andNauwerck 1993). We have also observed that Poterioo- chromonas spp. were present during toxic blooms of the cyanobacterium Microcystis in lakes of Thailand and P. R. China (unpublished data). Therefore, herbivory may be a common behavior among mixotrophic chrysomonads. Because of their ability to graze a wide size range of prey, mixotrophic chrysomonads may be effective competi- tors with other grazers for pico- and nanoplanktonic al- gae other than bacteria and may make a stronger link transferring energy of phytoplanktonic algae and bacte- ria to nanoplankton grazers by increasing trophic effi- ciency. Our observations and those in the literature im- ply that mixotrophic chrysomonads can influence not only the population dynamics and community composi- tion of bacteria, but also pico- and nanoplankton algae. Various factors influence both the ingestion and growth rates of mixotrophic chrysomonads, including prey density, light, pH, inorganic nutrients, and dis- solved organic carbon (Bird and Kalff 1987, 1989, Andersson et al. 1989, Sanders et al. 1990, Caron et al. 1990, 1993, Holen 1999); among these light has been studied in most detail. Light had a marked effect on the ingestion rate and growth of Dinobryon cylindricum (Caron et al. 1993). Dinobryon cylindricum cultured at a light intensity � 150 �mol photons�m�2�s�1 had inges- tion rates of approximately 5–10 bacteria�flagellate�1�h�1 during the exponential growth phase; however, when cultured in the dark D. cylindricum rapidly declined in density and ceased ingesting bacteria (Caron et al. 1993). We also observed that another species of Dino- bryon, D. sociale, and Uroglena americana were incapable of growth and ingestion in continuous dark with bac- teria as prey (unpublished data). The presence or ab- sence of light, in contrast, had no direct effect on phago- trophy for Ochromonas sp. or P. malhamensis (Andersson et al. 1989, Caron et al. 1990, Sanders et al. 1990, Sib- bald and Albright 1991). The ingestion and growth rates in both light and dark were the same when bac- teria were added as prey (Andersson et al. 1989, Caron et al. 1990, Sanders et al. 1990). In the present study there was no significant differ- ence in grazing and growth rates between phagotro- phy and mixotrophy during the exponential growth phase, indicating that light had no effect on P. malha- mensis during this period. This appears similar to ob- servations in previous studies on the same species and on Ochromonas sp. (Andersson et al. 1989, Caron et al. Table 3. Poterioochromonas malhamensis comparisons of maximum ingestion rate (cells�flag.�1�h�1) and averaged ingestion rate (cells�flag.�1�h�1, during exponential growth phase) for mixotrophic (light) and phagotrophic (dark) cells. Prey (�m) Treatment Max. ingestion rate Ingestion rate Microcystis viridis (5.6) Light 3.2 � 0.4 0.27 � 0.01 Dark 3.9 � 0.8 0.25 � 0.04 Chlorella pyrenoidosa (13.3) Light 1.8 � 0.5 0.18 � 0.02 Dark 1.2 � 0.4 0.18 � 0.01 Means � SD (n � 3, based on three replicate cultures) are not significantly different between the light and dark treatments with the same prey (P 0.05) but are significantly different between two kinds of prey (P � 0.05). GRAZING AND GROWTH OF P. MALHAMENSIS 743 1990, Sanders et al. 1990). However, our populations of P. malhamensis were incapable of growth and inges- tion in continuous dark for a period longer than 5 days with M. viridis or C. pyrenoidosa. During the sta- tionary phase, cell numbers of P. malhamensis were nearly constant, whereas decrease in prey density was observed. In contrast, there was a gradual decrease in cell density of P. malhamensis and no change or a slight increase in prey density in continuous dark. We confirmed that light is an important factor affecting phagotrophy of P. malhamensis by adding prey again on day 4 for a phagotrophic experiment (Fig. 3). In this case, the increase in density of the predator was probably due not only to the prey but also the light, because the population of P. malhamensis kept in con- tinuous dark had not yet increased after the addition of a high density of prey. Five days in the dark may have been the tolerance threshold of P. malhamensis in our study. It is therefore concluded that although P. malhamensis is light tolerant, it is also dependent on light for sustained phagotrophy. This conclusion dif- fers from those of previous studies (Andersson et al. 1989, Caron et al. 1990, Sanders et al. 1990). All cul- tures for determining ingestion and growth rates in our study were incubated for more than 8 days, whereas ingestion rates were measured during the first sampling interval by Caron et al. (1990) and dur- ing 52–70 hours by Sanders et al. (1990). Based on the above results, it is suggested that the measure- ments by Caron et al. and Sanders et al. were deter- mined within the tolerance threshold for light. Light tolerance of mixotrophic chrysomonads may vary with species. Dinobryon cylindricum, D. sociale, and U. americana are very light sensitive (Caron et al. 1993, our unpub- lished data), whereas Ochromonas and Poterioochromonas have a strong tolerance for light (Andersson et al. 1989, Caron et al. 1990, Sanders et al. 1990, this study). The present study agrees with the hypothesis that there is a requirement for some factor(s) supplied by photosyn- thesis in mixotrophic chrysomonads for phagotrophy (Caron et al. 1993). X. Z. was supported by a National Institute Postdoctoral Fellowship Award from the Research Development Corporation of Japan. Andersson, A., Falk, S., Samuelsson, G. & Hagström, Å. 1989. Nutri- tional characteristics of a mixotrophic nanoflagellate, Ochromo- nas sp. Microb. Ecol. 17:252–62. 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