Limnol. Oceanogr., 56(6), 2011, 000–000 2011, by the American Society of Limnology and Oceanography, Inc. doi:10.4319/lo.2011.56.6.0000 E Resting egg production induced by food limitation in the calanoid copepod Acartia tonsa Guillaume Drillet,a,b,1,* Benni W. Hansen,b and Thomas Kiørboea a Danish Technical University (DTU Aqua), National Institute of Aquatic Resources, Charlottenlund, Denmark of Environmental, Social and Spatial Change (ENSPAC), Roskilde University, Roskilde, Denmark b Department Abstract ; Three populations of the copepod Acartia tonsa, two from the Baltic Sea and one from the U.S. East Coast, were compared for resting egg production at conditions of saturating and limiting food availability. All three populations produced eggs that hatched within 72 h when incubated at 17uC (subitaneous eggs), but the two Baltic populations in addition produced eggs that hatched at a much slower rate, in the course of a month (delayed hatching eggs [DHE]). Such eggs were not produced by the U.S. population. The fraction of DHE increased when food was limiting. Females from a Baltic population that were incubated individually all produced subitaneous eggs, but about half the females consistently also produced DHE. Cold storage that mimicked boreal winter conditions synchronized the hatching of DHE after extended storage, indicating that spring hatching of DHE might seed the water column with nauplii as an adaptation to match the timing of the spring bloom in boreal marine ecosystems. Low food availability promotes the production of resting eggs in marine copepods. hatching is not possible even if environmental conditions are suitable. After termination of the refractory period, eggs can hatch or remain quiescent if the environmental conditions are un-suitable. A third category of eggs was later described (Chen and Marcus 1997) and is referred to as delayed hatching eggs (DHE). They do not belong to either of the two established categories because the hatching is not fast enough to consider the eggs as subitaneous and the refractory period is not long enough to categorize the eggs as true diapause eggs. The DHE category may be controlled through the same gene expression pathway as for those defined as true diapause eggs and may simply represent different torpidity levels, as proposed for freshwater cyclopoid copepods (Elgmork 1996). These eggs may be considered as eggs going through oligopause (Alekseev et al. 2007). Diapause, quiescent, and DHE eggs are all commonly called resting eggs. Cues used for diapause induction have been described in the literature for a wide range of aquatic organisms: for copepods, mainly abiotic cues (e.g., light and temperature); rotifers, cues from the biotic environment (e.g., food quality, quantity, and crowding); and cladocerans, a mix of both types (Gyllstrom and Hansson 2004). It is less obvious whether the production of resting eggs is induced by biotic cues in calanoid copepods. It has been suggested that induction of resting stages could be density dependent and due to the accumulation of metabolites in the water (Ban and Minoda 1994). Production of resting stages under crowded condition has also been described for other crustaceans, as, for example, Daphnia lumholtzi (Smith et al. 2009). However, the link between laboratory studies examining the population density effects on resting egg production in marine copepods and the occurrences of high density swarms in nature has never been properly studied, even though high densities occur frequently in the natural environment (Devreker et al. 2008). Life history strategies may be adapted to unstable environments in various ways. Under stressful environmental conditions, mobile species can migrate to more suitable places, but migration in time by going into dormancy is also a suitable strategy to allow survival (Hairston and Bohonak 1998). Saving genes over time is the principle behind dormancy. Dormancy is a widespread life history adaptation in the plankton, both among phytoplankton and zooplankton. Phytoplankton, for example, produces resting spores that may survive unproductive seasons in the sediment (Hallegraeff and Bolch 1992). For zooplankton, dormancy is often more prevalent in freshwater as compared to marine environments, due to the typically larger fluctuations in limnic habitats. However, some marine crustaceans are known to rest (Alekseev et al. 2007); and, among marine copepods, diapause has been described for adult, copepodite, and egg stages (Mauchline et al. 1998). Diapausing in eggs has been described in close to 50 species of calanoid copepods (Engel and Hirche 2004) that all belong to the superfamily of Centropagoidea. Most if not all of these species are neritic and, thus, occur in habitats with rather large environmental variability. Different types of eggs have been described for copepods, and Grice and Marcus (1981) proposed a definition separating two categories of eggs. Subitaneous eggs hatch immediately after spawning under optimal conditions but are in some species able to arrest development and remain in a quiescent stage if the environmental conditions are unsuitable. Such eggs will continue embryogenesis and eventually hatch as soon as the environmental conditions become favorable. Diapause eggs go through a long, hormonally controlled refractory period during which * Corresponding author: [email protected] 1 Present address: DHI Water and Environment Pte. Ltd., Singapore, Singapore 0 Limnology limn-56-06-08.3d 11/8/11 14:56:07 1 Cust # 11-106 0 Drillet et al. In this study, we use the copepod Acartia tonsa, a cosmopolitan euryhaline and eurytherm calanoid that often dominates the zooplankton community in coastal waters. The species is known to produce dormant eggs, as either quiescent, true diapause, or DHE (Zillioux and Gonzalez 1972; Castro-Longoria 2001; Katajisto 2006). We examine the effect of food availability on the production of resting eggs and characterize the hatching dynamics of resting eggs as a function of the duration of their dormancy. Using laboratory cultures stemming from three populations that are adapted to different seasonal environments, we further study population differences in the induction of resting egg production. Two of these populations (from the Baltic Sea area) originate from the same mitochondrial clade, while a population from Florida is genetically distinct (16S ribosomal RNA and cytochrome oxidase subunit I; Drillet et al. 2008a).We hypothesize that food limitation induces production of resting eggs and that the induction differs among populations adapted to different environments. Methods Experimental animals and cultures—Three A. tonsa cultures originating from Kiel Bright (Germany), Øresund (Denmark), and Florida were compared in a common garden experiment for resting egg production. The experimental cultures were initiated with eggs from the source cultures. Eggs from the source cultures were refrigerated and sent by express mail (, 2 d) to our laboratory at the Danish Technical University, where the experimental cultures were established immediately. The Øresund culture originated from individuals isolated in 1981 from the Øresund (56uN; 12uE). The population has been kept at 30 salinity, 17uC, and dim constant light and fed 30,000– 60,000 cell mL21 every 2 d with the haptophyte Rhodomonas salina. The Kiel culture originates from adults isolated August 2003 from the Kiel Bight in the southwestern Baltic Sea (54uN; 10uE; Holste and Peck 2005). The culture has been kept at 18 salinity, 18uC and 13 : 11 light : dark (LD), and fed daily Rhodomonas sp. at 50,000 cell mL21. The Florida culture was collected from local waters outside the Florida State University Coastal and Marine Laboratory (30uN; 84uW) between 2002 and 2004. The culture was maintained in the laboratory at salinity 30, 17uC, and 14 : 10 LD, and fed daily a mixed algal diet (Rhodomonas lens, R. salina, and occasionally Akashiwo sanguinea; 30,000–50,000 cell mL21). Eggs from all cultures were regularly harvested, rinsed, and stored in test tubes at 1–3uC for later use. Cultures of the three populations were established in 30liter tanks and run under similar and constant laboratory conditions for two generations to eliminate parental effects (17.6uC 6 0.3uC, 34 salinity, 12 : 12 LD, fed in excess with R. salina). Eggs were then harvested to establish the experimental cultures. When copepodites appeared, animals from each population were separated into two groups that were fed different amounts of phytoplankton. The first group, labeled low food, was offered 2000 cell mL21, and the high food group was offered 40,000 cell mL21 (subsaturated vs. saturated, Berggreen et al. 1988). Food Limnology limn-56-06-08.3d 11/8/11 14:56:07 2 Cust # 11-106 concentrations were adjusted twice daily, and the seawater in all six tanks was changed weekly. When adults appeared in the tanks, eggs were harvested to initiate the hatching experiments. The density of copepods in the tanks varied between 200 to 700 individuals per liter (mix of copepodites and adults), and the density was always higher under high food treatments than under low food treatments. Hatching experiments—Eggs were harvested when less than 2 h old by harvesting eggs 1.5 h after a preliminary harvest and were washed on a sieve. Harvested eggs were distributed among 10 small Petri dishes (from 47 to 205 eggs per dish, 17.6uC 6 0.3uC, 34 salinity, 12 : 12 LD), and hatched eggs (nauplii) were regularly counted under a dissection microscope (Olympus SZ 40) for approximately 72 h (subitaneous eggs). Unhatched eggs were then transferred to 10 new Petri dishes, while the nauplii were fixed in 1% final concentration of acid Lugol’s and counted. The new Petri dishes were inspected daily for more than a month, and eggs and nauplii were counted and nauplii removed. Every 2 or 3 d, the eggs were transferred to new Petri dishes with clean water in order to minimize the development of fungi or bacteria on the egg shells. Individual variation—Incubations of Kiel females were carried out under optimal conditions (saturated food, Berggreen et al. 1988) to examine whether individual females were consistently producing the same type of eggs. Thirty females bearing a spermatophore were incubated individually under high-food conditions in 600-mL glass bottles. The bottles were mounted on a plankton wheel (0.5 round per minute) for two days. Each day, the content of each bottle was emptied through a set of two sieves (180mm and 53-mm mesh size) to separate females from eggs, and the female was reincubated in a fresh suspension of algae. Eggs were counted and incubated for 72 h for hatching and then fixed in Lugol’s. Nauplii and remaining eggs were then counted to calculate the number of hatched eggs (subitaneous eggs), decayed (nonviable) eggs, and nonhatching eggs, which were considered as DHE. Decaying eggs are easily distinguished from nonhatched ones on the basis of attached bacteria and a clear, not dark, egg interior. Effect of resting duration on hatching success—DHE from the Kiel population were produced by collecting live eggs that had not hatched for 5 d. These eggs were stored in 2-mL Eppendorff tubes (500 eggs per tube) in the dark at 1.5uC. Every month, samples of these eggs were transferred to 17uC, and their hatching success was examined after 48-h incubation at constant dim light. Constant light is reported to increase the 48-h hatching success of A. tonsa (Peck et al. 2008). Results Egg types and food conditions—Eggs exhibited two types of hatching patterns: a group of eggs hatched within 72 h (subitaneous) and another group hatched slowly, in the Acartia tonsa resting egg induction 0 was highest at the low food concentration (Fig. 1). Also, for the Baltic populations, the 72-h hatching success was lower for the eggs produced under low food concentration than under high food concentration (Mann–Whitney rank sum test, t 5 140,000, n 5 10, p 5 0.009 [Øresund]; t 5 148,000, n 5 10, p 5 0.001 [Kiel]). The Florida population did not survive the low-food treatment. The Kiel population produced relatively more DHE than the Øresund population, and the maximum hatching success of DHE occurred in the Kiel population, whatever the food treatment. A fraction of the eggs never hatched but decayed and, hence, were dead. Fig. 1. Final hatching success after 72 h (subitaneous eggs) and after 1 month (delayed hatching eggs) in three populations of Acartia tonsa raised under different food conditions (low: 2000 cell mL21 and high: 40,000 cell mL21 of Rhodomonas salina) in a common garden experiment. course of about 1 month (DHE). The two Baltic populations produced both types of eggs, while the Floridian population never produced DHE (Figs. 1, 2). For both of the Baltic populations, the proportion of DHE Individual variation—There was significant variation between individuals in their tendency to produce DHE, as examined for the Kiel population (Fig. 3). Over the 2-d incubations, all individual females produced subitaneous eggs, and approximately half the females also produced DHE. It was the same females that produced DHE on the first and second day of the incubation: of the 12 females producing DHE on the second day, 17 had produced DHE also on the first day. Effect of cold storage—The 48-h hatching success of coldstored DHE from the Kiel population varied with the duration of the storage period: it increased during the first 5 months, from 0 to 83% 6 22%, whereupon it decreased until no more hatching occurred after 12 months (Fig. 4). Samples incubated for 14 and 22 months also showed no hatching. The eggs that had been cold-stored for 1 month were allowed to hatch beyond the 48 h, and, in the course of the subsequent 500 h, 84% 6 5% of these eggs hatched (Fig. 5). Thus, the Fig. 2. Hatching of delayed hatching eggs over 1.5-month period in two populations of Acartia tonsa fed at high and low food levels (subitaneous eggs that hatched within 72 h have been removed). Limnology limn-56-06-08.3d 11/8/11 14:56:08 3 Cust # 11-106 0 Drillet et al. Fig. 3. Egg categories produced over 2 consecutive days by 30 individual females of Acartia tonsa from the Kiel population. effect of cold storage was to reduce the hatching period, from about 1 month prior to storage, to 10 d after 1 month of storage, and to only about 48 h after 5 months of storage. In all cases, the total hatching success was the same, . 80% Limnology limn-56-06-08.3d 11/8/11 14:56:16 4 Cust # 11-106 (Fig. 2, Kiel high food treatment, Figs. 4, 5). Eggs that had been stored for . 12 months never hatched, even after 1 month of incubation, and many had died during storage (58% after 14 months and 99% after 22 months). < Acartia tonsa resting egg induction Fig. 4. Hatching success of Acartia tonsa DHE eggs at 17uC and normoxia for 48 h (mean 6 SD) after months of storage in the dark at 1.5uC. Data after 22 months of storage showed no hatching. Discussion Delayed hatching was proposed for Labidocera scotti and Pontella meadi by Chen and Marcus (1997) in the Gulf of Mexico and for A. tonsa in the northern Baltic Sea (Katajisto 2006) and in our culture (Drillet et al. 2008b). However, the present study is the first to document DHE and examine the factors that induce their production. One difficulty that previous studies had in identifying the presence of DHE was that egg incubation times for estimation of hatching rates and success had been based on models of hatching speed related to temperature (McLaren et al. 1969; see review by Mauchline et al. 1998). Thus, the incubation time used to estimate hatching success of A. tonsa eggs, for example, has most often been limited to approximately 48 h at 17–18uC (Jonasdottir and Kiørboe 1996; Vargas et al. 2006) and has sometimes been increased to 5 d when incubated at lower temperature (Castro-Longoria 2003); and unhatched eggs have been considered nonviable, while in fact they may have been DHE. This also implies that, in many studies, the hatching success of A. tonsa eggs was potentially underestimated and could have biased conclusions. This is particularly relevant for studies looking at the effect of phytoplankton quantity, quality, and toxicity on hatching success (Jonasdottir and Kiørboe 1996; Vargas et al. 2006). The production of DHE was increased by low food availability, suggesting that food quantity in the environment is a cue for the production of DHE, as described for resting egg production in other aquatic invertebrates (Gilbert and Schreiber 1998) as well as for summer diapause induction of nauplii stages of freshwater cyclopoid copepods (Santer and Lampert 1995). Other factors that we did not examine may similarly induce DHE production, such as low temperatures, low light, or copepod density. In another copepod, Eurytemora affinis, resting egg production is induced via infochemicals in water in which high population density occurred (Ban and Minoda 1994). We argue that this was not a major Limnology limn-56-06-08.3d 11/8/11 14:56:30 5 Cust # 11-106 0 Fig. 5. Hatching success as a function of time of delayed hatching eggs after a month of storage in the dark at 1.5uC (mean 6 SD). mechanism in our experiments because the density of copepods was always higher in the high-food treatment than in the low-food treatment conditions and, thus, would have countered any effect of food density. However, even under optimal conditions, a significant fraction of the eggs in the Baltic population were DHE, suggesting that DHE production is a risk-spreading strategy. The eggs that still looked viable after 14 months of storage, but that did not hatch, survived for another month at 17uC before decaying. Nonviable eggs of A. tonsa normally degrade very rapidly at 17uC, suggesting that the unhatched eggs were still viable but lacked a relevant environmental cue for hatching. Their hatching may also have been restricted by the limited presence of ecdysteroids (i.e., molting hormones), which are believed to play an important role in diapause formation and exit (Johnson 2003). The 14 and 22 months of cold storage of DHE in the dark were lethal for 58% and 99% of the incubated eggs, respectively, and DHE are thus not produced as a strategy to survive very long periods in the sediment, as has been reported for diapause eggs (Marcus et al. 1994; Hairston et al. 1995). Also, DHE is not a pluri-annual hatching strategy, as described for plants as a bet-hedging response to highly fluctuating environments (Philippi 1993). Individual females were capable of producing subitaneous eggs and DHE simultaneously. This is an example of a risk-spreading strategy, as similarly described for rotifers by Gilbert and Schreiber (1998), with the purpose of ensuring gene spreading in fluctuating environments. The production of DHE reduces the risk of egg hatching at unfavorable (low-food) conditions and allows the females to spread their offspring in the short-term future without taking the risk associated with deep burial of eggs in the sediment. The latter is one of the reasons for the decrease of eggs in an egg bank over time (Caceres and Tessier 2003; De Stasio 2007). Production of DHE also increases the spatial spreading potential, particularly in areas where ocean currents are significant. An extended period of cold 0 Drillet et al. and dark conditions (as hypothetically experienced in the sediment) increases the synchrony of the hatching when later facing optimal conditions. Synchronous hatching and cohort development increase the chances of reaching maturity simultaneously with conspecifics and therefore increase the chances of encountering a mate. This may in particular be important when hatching nauplii colonize the water column during spring. The production of DHE gives A. tonsa a great potential to invade new habitats via egg spreading and ballast water. In fact, A. tonsa invaded European waters from the United States and was first described in European water by Rémy (1927) in Normandy, France. Genetic markers suggest that the Baltic population of A. tonsa likely originates from a native population off Rhode Island (Drillet et al. 2008a). The production of DHE under similar culture conditions was different among the examined populations. The Floridian population was not capable of producing DHE eggs under the tested food availability, but it is known to survive harsh condition as quiescent eggs for up to a month (Drillet et al. 2007, 2008a). This population originates from a different mitochondrial clade than the two other studied populations and may not exhibit the same life history traits. A. tonsa is present in Floridian water all year round, and, though it is possible to find resting eggs of A. tonsa in seagrass beds, there is no evidence that these are DHE (Scheef and Marcus 2010). Thus, the A. tonsa Florida population has apparently either lost or has not evolved the ability to produce DHE eggs. Because the Florida population did not survive at the low food concentration, we cannot entirely rule out the possibility that DHE are produced at low food availability. The apparent inability to produce DHE eggs is correlated to a difference in egg size: the eggs of the Florida populations have a 20% smaller volume than the eggs of the two Baltic populations (Drillet et al 2008a). Eggs produced by females from the Floridian population do not need high reserves to overwinter or rest, and therefore a female could potentially produce more eggs as a trade-off. The difference in egg size is suggestive of the cost of producing eggs that can rest for extended periods. The two Baltic populations originate from the same mitochondrial clade (Drillet et al. 2008a) and come from areas very near to each other with strong ocean currents; we therefore doubt that they are genetically isolated in nature, yet they differed somewhat with respect to production of DHE. The differences may have evolved during the 30 yr of culturing the Øresund population (. 250 generations), in which the selective advantage of producing DHE may have been very limited. Selection pressure has already been shown to alter the behavioral pattern in the same laboratory population, in which the individuals have partly lost their diel rhythm (Tiselius et al. 1995). Delayed hatching strategy (oligopause) is a very important life history trait that allows the spread of hatching over a relatively short period of time (a month or two), increasing the likelihood that some offspring will encounter good conditions and decreasing the risk of deep burial in the sediment. Hatching after a delay of a few weeks allows early nauplii to evolve in an environment in which the previous generation is likely to have died out, limiting the Limnology limn-56-06-08.3d 11/8/11 14:56:36 6 Cust # 11-106 competition for resources. Moreover, synchronous hatching after a cold period (winter) likely increases the chances of successful mating when reaching adulthood. To our knowledge, the present observations are the first describing the effect of food limitation on resting egg production in marine copepods. These observations support previous work on other organisms that are known to produce resting stages under food limitation, strongly suggesting that this particular cue could be universal for promoting resting egg production in invertebrates. Acknowledgments We are indebted to Linda Holste and Cris Oppert for receiving eggs from their copepod cultures and the two reviewers for their pertinent comments. The present project was carried out through a Ph.D. grant to Guillaume Drillet and was funded by the Eur-Oceans network of excellence, The Graduate School of Stress Studies (GESS), and Roskilde University and the Danish Council for Independent Research Postdoctoral grant 10-094773. TK and BWH were supported by The Danish Council for Independent Research. References ALEKSEEV, V. R., B. T. DE STASIO, AND J. J. GILBERT [EDS.]. 2007. Diapause in aquatic invertebrates: Theory and human use. Monographiae biologicae, v. 84. Springer. BAN, S., AND T. MINODA. 1994. Induction of diapause egg production in Eurytemora affinis by their own metabolites. Hydrobiologia 292/293: 185–189, doi:10.1007/BF00229940 BERGGREEN, U., B. HANSEN, AND T. KIØRBOE. 1988. Food size spectra, ingestion and growth of the copepod Acartia tonsa during development: Implications for determination of copepod production. Mar. Biol. 99: 341–352, doi:10.1007/ BF02112126 CACERES, C. E., AND A. J. TESSIER. 2003. How long to rest: The ecology of optimal dormancy and environmental constraint. Ecology 84: 1189–1198, doi:10.1890/0012-9658(2003) 084[1189:HLTRTE]2.0.CO;2 CASTRO-LONGORIA, E. 2001. Comparative observations on the external morphology of subitaneous and diapause eggs of Acartia species from Southampton water. Crustaceana 74: 225–236, doi:10.1163/156854001505479 ———. 2003. Egg production and hatching success of four Acartia species under different temperature and salinity regimes. J. Crustac. Biol. 23: 289–299, doi:10.1651/0278-0372 (2003)023[0289:EPAHSO]2.0.CO;2 CHEN, F., AND N. H. MARCUS. 1997. Subitaneous, diapause, and delayed-hatching eggs of planktonic copepods from the northern gulf of Mexico: Morphology and hatching success. Mar. Biol. 127: 587–597, doi:10.1007/s002270050049 DE STASIO, B. T. 2007. Egg bank formation by aquatic invertebrates, p. 121–133. In V. R. Alekseev, B. T. De Stasio, and J. J. Gilbert [eds.], Diapause in aquatic invertebrates: Theory and human use. Monographiae biologicae, v. 84. Springer. DEVREKER, D., S. SOUISSI, J. C. MOLINERO, AND F. NKUBITO. 2008. Trade-offs of the copepod Eurytemora affinis in mega-tidal estuaries: Insights from high frequency sampling in the Seine Estuary. J. Plankton Res. 30: 1329–1342, doi:10.1093/plankt/ fbn086 DRILLET, G., E. GOETZE, P. M. JEPSEN, J. K. HøJGAARD, AND B. W. HANSEN. 2008a. Strain-specific vital rates in four Acartia tonsa cultures, I: Strain origin, genetic differentiation and egg survivorship. Aquaculture 280: 109–116, doi:10.1016/j.aquaculture. 2008.04.005 Acartia tonsa resting egg induction = ———, P. M. JEPSEN, J. K. HØJGAARD, N. O. G. JØRGENSEN, AND B. W. HANSEN. 2008b. Strain-specific vital rates in four Acartia tonsa cultures, II: Life history traits and biochemical contents of eggs and adults. Aquaculture 279: 47–54, doi:10.1016/j.aquaculture.2008.04.010 ———, L. C. LINDLEY, A. MICHELS, J. WILCOX, AND N. H. MARCUS. 2007. Improving cold storage of subitaneous eggs of the copepod Acartia tonsa Dana from the Gulf of Mexico (USA-Florida). Aquacult. Res. 38: 457–466, doi:10.1111/ j.1365-2109.2007.01673.x ELGMORK, K. 1996. Variation in torpidity of diapause in freshwater cyclopoid copepods. Hydrobiologia 320: 63–70, doi:10.1007/BF00016805 ENGEL, M., AND H. J. HIRCHE. 2004. Seasonal variability and inter-specific differences in hatching of calanoid copepod resting eggs from sediments of the German Bight (North Sea). J. Plankton Res. 26: 1083–1093, doi:10.1093/plankt/fbh099 GILBERT, J. J., AND D. K. SCHREIBER. 1998. Asexual diapause induced by food limitation in the rotifer Synchaeta pectinata. Ecology 79: 1371–1381. GRICE, G. D., AND N. H. MARCUS. 1981. Dormant eggs of marine copepods. Oceanogr. Mar. Biol. Annu. Rev. 19: 125–140. GYLLSTROM, M., AND L. A. HANSSON. 2004. Dormancy in freshwater zooplankton: Induction, termination and the importance of benthic-pelagic coupling. Aquat. Sci. 66: 274–295, doi:10.1007/s00027-004-0712-y HAIRSTON, N. G., AND A. J. BOHONAK. 1998. Copepod reproductive strategies: Life-history theory, phylogenetic pattern and invasion of inland waters. J. Mar. Sys. 15: 23–34, doi:10.1016/ S0924-7963(97)00046-8 ———, R. A. VAN BRUNT, AND C. M. KEARNS. 1995. Age and survivorship of diapausing eggs in a sediment egg bank. Ecology 76: 1706–1711, doi:10.2307/1940704 HALLEGRAEFF, G. M., AND C. J. BOLCH. 1992. Transport of diatom and dinoflagellate resting spores in ship ballast water: Implications for plankton biogeography and aquaculture. J. Plankton Res. 14: 1067–1084, doi:10.1093/plankt/14.8.1067 HOLSTE, L., AND M. PECK. 2005. The effects of temperature and salinity on egg production and hatching success of Baltic Acartia tonsa (Copepoda: Calanoida): A laboratory investigation. Mar. Biol. 148: 1–10, doi:10.1007/s00227-005-0060-z JOHNSON, C. L. 2003. Ecdysteroids in the oceanic copepod Calanus pacificus: Variation during molt cycle and change associated with diapause. Mar. Ecol. Prog. Ser. 257: 159–165, doi:10.3354/meps257159 JONASDOTTIR, S., AND T. KIØRBOE. 1996. Copepod recruitment and food composition: Do diatoms affect hatching success? Mar. Biol. 125: 743–750, doi:10.1007/BF00349257 KATAJISTO, T. 2006. Benthic resting eggs in the life cycles of calanoid copepods in the northern Baltic Sea. Ph.D. thesis. Univ. of Helsinki. MARCUS, N. H., AND C. M. FULLER. 1986. Subitaneous and diapause eggs of Labidocera aestiva Wheeler (Copepoda, Calanoida): Differences in fall velocity and density. J. Exp. Mar. Biol. Ecol. 99: 247–256, doi:10.1016/0022-0981(86) 90226-1 Limnology limn-56-06-08.3d 11/8/11 14:56:39 7 Cust # 11-106 0 ———, R. LUTZ, W. BURNETT, AND P. CABLE. 1994. Age, viability, and vertical distribution of zooplankton resting eggs from an anoxic basin: Evidence of an egg bank. Limnol. Oceanogr. 39: 154–158, doi:10.4319/lo.1994.39.1.0154 MAUCHLINE, J., J. H. S. BLAXTER, A. J. SOUTHWARD, AND P. A. TYLER. 1998. The biology of calanoid copepods. Elsevier Academic Press. MCLAREN, I. A., C. J. CORKETT, AND E. J. ZILLIOUX. 1969. Temperature adaptations of copepod eggs from Arctic to tropics. Biol. Bull. 137: 486–493, doi:10.2307/1540170 PECK, M. A., B. EWEST, L. HOLSTE, P. KANSTINGER, AND M. MARTIN. 2008. Impacts of light regime on egg harvests and 48h egg hatching success of Acartia tonsa (Copepoda: Calanoida) within intensive culture. Aquaculture 275: 102–107, doi:10.1016/j.aquaculture.2007.12.008 PHILIPPI, T. 1993. Bet-hedging germination of desert annuals: Beyond the first year. Am. Nat. 142: 474–487, doi:10.1086/ 285550 RÉMY, P. 1927. Note sur un copépode de l’eau saumâtre du canal de Caen a la mer. Acartia (Acanthacartia) tonsa Dana. Ann. Biol. Lacustre 15: 169–186. [Note on a brackish copepod in the canal between Caen and the sea: Acartia (Acanthacartia) tonsa Dana.] SANTER, B., AND W. LAMPERT. 1995. Diapause in cyclopoid copepods: Adaptive response to a food bottleneck? J. Anim. Ecol. 64: 600–613, doi:10.2307/5803 SCHEEF, L. P., AND N. H. MARCUS. 2010. Occurrence and significance of copepod resting egg accumulation in seagrass sediments. Mar. Ecol. Prog. Ser. 407: 125–134, doi:10.3354/ meps08573 SMITH, A. S., K. ACHARYA, AND J. JACK. 2009. Overcrowding, food and phosphorus limitation effects on ephipphia production and population dynamics in the invasive species Daphnia lumholtzi. Hydrobiologia 618: 47–56, doi:10.1007/ s10750-008-9546-2 TISELIUS, P., B. HANSEN, P. JONSSON, T. KIøRBOE, T. G. NIELSEN, S. PIONTKOVSKI, AND E. SAIZ. 1995. Can we use laboratory reared copepods for experiments?: A comparison of feeding behavior and reproduction between a field and a laboratory population of Acartia tonsa. ICES J. Mar. Sci. 52: 369–376, doi:10.1016/ 1054-3139(95)80052-2 VARGAS, C. A., R. ESCRIBANO, AND S. POULET. 2006. Phytoplankton food quality determines time windows for successful zooplankton reproductive pulses. Ecology 87: 2992–2999, doi:10.1890/0012-9658(2006)87[2992:PFQDTW]2.0.CO;2 ZILLIOUX, E. J., AND J. G. GONZALEZ. 1972. Egg dormancy in a neretic calanoid copepod and its implications to overwintering in boreal waters, p. 217–230. In B. Battaglia [ed.], Proceedings of the Fifth European Marine Biology Symposium. Piccin. Associate editor: Michael R. Landry Received: 08 March 2011 Accepted: 20 July 2011 Amended: 22 July 2011 0 Drillet et al. Authors Queries Journal: Limnology Paper: limn-56-06-08 Title: Resting egg production induced by food limitation in the calanoid copepod Acartia tonsa Dear Author During the preparation of your manuscript for publication, the questions listed below have arisen. Please attend to these matters and return this form with your proof. Many thanks for your assistance Query Reference Query 1 Author: This article has been lightly edited for grammar, style, and usage. Please compare it with your original document and make corrections on these pages. Please limit your corrections to substantive changes that affect meaning. If no change is required in response to a question, please write ‘‘OK as set’’ in the margin. Copy editor 2 Author: In sentence beginning ‘‘In all cases, the total hatching….,’’ please clarify placement of phrase ‘‘Kiel high food treatment’’ – how does it relate to the figure citations? Copy editor 3 Author: Please cite Marcus and Fuller 1986 in the text. Copy editor Limnology limn-56-06-08.3d 11/8/11 14:56:39 Remarks 8 Cust # 11-106
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