2002 from Vexar⢠screens suspended for 1 month from a floating dock at Ford Island,. Pearl Harbor, Hawaii. The sex of each worm was determined and ...
LIFE-HISTORY CONSEQUENCES OF ARTIFICIAL SELECTION FOR INCREASED EGG SIZE IN Hydroides elegans (POLYCHAETA: SERPULIDAE)
By CECELIA MARIE MILES
A DISSERTATION PRESENTED TO THE GRADUATE SCHOOL OF THE UNIVERSITY OF FLORIDA IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF DOCTOR OF PHILOSOPHY UNIVERSITY OF FLORIDA 2006
Copyright 2006 by Cecelia Marie Miles
This work is dedicated to Dr. Larry McEdward. Larry’s ability to distill complex topics down to their essential elements served to focus my efforts as a new graduate student. As I have advanced in my career, I have come to respect this skill immensely and it is one that I aspire to emulate. This project was conceived and planned under his guidance and his influence is present in every aspect.
ACKNOWLEDGMENTS For insight, guidance, encouragement, and especially for leading by example, I thank Dr. Marta L. Wayne. I also thank committee members Dr. Colette St. Mary, Dr. Shirley Baker, and Dr. Gustav Paulay. I am especially grateful to Dr. Ben Bolker for his clear thinking and concise statistical advice. I thank Dr. Michael G. Hadfield for his generosity and advice, and everyone at Kewalo Marine Laboratory in Honolulu, Hawaii for their kokua. I could never have completed this project without my fellow “worm wrangler” at Kewalo, Sharon Kelly. I thank the Zoology Department at the University of Florida for financial, emotional, and spiritual support. I would also like to acknowledge the Auzenne Graduate Scholars Fellowship from the University of Florida, and the Grinter Fellowship from the Graduate School. I wish to thank my family and especially my husband, Myron G. Miles, for his infinite support.
iv
TABLE OF CONTENTS page ACKNOWLEDGMENTS ................................................................................................. iv LIST OF TABLES............................................................................................................ vii LIST OF FIGURES ........................................................................................................... ix ABSTRACT.........................................................................................................................x CHAPTER 1
GENERAL INTRODUCTION ....................................................................................1
2
ESTIMATES OF HERITABILITY FOR EGG SIZE IN THE SERPULID POLYCHAETE Hydroides elegans .............................................................................8 Introduction...................................................................................................................8 Material and Methods .................................................................................................11 Collection and Spawning.....................................................................................11 Half Sib Breeding Design....................................................................................14 Selection ..............................................................................................................16 Results.........................................................................................................................17 Discussion...................................................................................................................18
3
DIRECT AND INDIRECT RESULTS OF ARTIFICIAL SELECTION FOR INCREASED EGG SIZE IN THE SERPULID POLYCHAETE Hydroides elegans ........................................................................................................................24 Introduction.................................................................................................................24 Methods ......................................................................................................................29 Collection, Spawning, and Selection...................................................................29 Larval Size...........................................................................................................31 Juvenile Tube Length ..........................................................................................32 Total Egg Energy.................................................................................................32 Fecundity .............................................................................................................34 Adult Dry Weight ................................................................................................35 Data Analysis.......................................................................................................35 Results.........................................................................................................................36 Direct Response to Selection...............................................................................36
v
Correlated Responses to Selection ......................................................................36 Spontaneous Spawning and Sex Ratios...............................................................38 Discussion...................................................................................................................39 More + Bigger = Better… or Does It?.................................................................39 Conclusions and Future Directions .....................................................................44 4
CONCLUSIONS ........................................................................................................49
LIST OF REFERENCES...................................................................................................53 BIOGRAPHICAL SKETCH .............................................................................................67
vi
LIST OF TABLES page
Table 2-1
Number of females used to establish six individual lines in Generation 7 ..............21
2-2
Half-sib breeding design; Fully nested ANOVA and variance component analysis for egg diameter in Hydroides elegans.......................................................22
3-1
Egg diameter (µm) in replicate selected vs. control lines of Hydroides elegans after 4 generations of selection.................................................................................46
3-2
Total egg energy in replicate selected vs. control lines of Hydroides elegans (calculated as µg C egg-1).........................................................................................46
3-3
Absolute fecundity in replicate selected vs. control lines of Hydroides elegans (eggs female-1)..........................................................................................................47
3-4
Relative fecundity based on dry weight of the female in replicate selected vs. control lines of Hydroides elegans (eggs mg-1) .......................................................47
3-5
Adult female dry weight (mg) in replicate selected vs. control lines of Hydroides elegans......................................................................................................................47
3-6
Larval volume (µL) at 18 to 20 h post-fertilization in replicate selected vs. control lines of Hydroides elegans...........................................................................47
3-7
Volume (µL) of competent (5 d) larvae in replicate selected vs. control lines of Hydroides elegans ....................................................................................................47
3-8
Juvenile tube length (mm) at 21 d in replicate selected vs. control lines of Hydroides elegans ....................................................................................................47
3-9
Summary of direct and correlated responses to selection for increased egg diameter in replicate selected v controls lines of Hydroides elegans ......................48
3-10 Effect of selection (treatment) on the relative numbers of males and females in Generations 7 to 11 ..................................................................................................48 3-11 Mean percent females present at spawning (6 weeks post-fertilization) in replicate selected vs. control lines of Hydroides elegans.........................................48
vii
4-1
Phenotypic correlations between the trait of egg size and a suite of life-history traits in replicate selected and control lines in the polychaete Hydroides elegans ..52
viii
LIST OF FIGURES page
Figure 2-1
Response to direct selection on egg diameter for four generations of in the polychaete Hydroides elegans..................................................................................22
2-2
Mean egg diameter (± SE) before and after direct selection for increased egg diameter in replicate selected (1,3,5) and control (2,4,6) lines of Hydroides elegans......................................................................................................................23
3-1
Cumulative response to selection for increased egg diameter in H. elegans was positive through Generation 11 ................................................................................46
ix
Abstract of Dissertation Presented to the Graduate School of the University of Florida in Partial Fulfillment of the Requirements for the Degree of Doctor of Philosophy LIFE-HISTORY CONSEQUENCES OF ARTIFICIAL SELECTION FOR INCREASED EGG SIZE IN Hydroides elegans (POLYCHAETA: SERPULIDAE) By Cecelia M. Miles May 2006 Chair: Marta L. Wayne Department: Zoology Goals of this study were to estimate narrow-sense heritability (h2) for egg size in the polychaete worm Hydroides elegans, to examine direct and correlated responses to selection on increased egg size in a suite of life-history characters, and to explore how these correlations changed as egg size was increased by artificial selection. Narrow-sense heritability is a predictor of short-term response to selection. Many quantitative models have invoked selective response in egg size as a key transitional element in the evolution of life histories in marine invertebrates, assuming that egg size can and does respond to selection. I tested this assumption using a half-sib breeding design and obtained an estimate for h2 of 0.45 for egg size in a Pearl Harbor, HI population. I performed four generations of artificial selection for increased egg size that allowed me to estimate cumulative realized heritability in the same population as 0.58. Artificial selection resulted in a direct response of 2.5 σP in egg size relative to the common base population. Though I predicted negative correlated responses in some
x
traits under selection, none was measured. A positive correlated response to selection was observed in fecundity, total egg energy, and larval size at competence, relative to control lines. No significant correlated response was observed in early larval size, juvenile tube length, or adult dry weight. H. elegans is a protandrous hermaphrodite, and sex ratio data across generations indicated that large-egg selected lines were changing sex earlier than control lines. I propose that this earlier sex change resulted in selected individuals spending less time as males relative to controls, consequently decreasing their overall fitness. Phenotypic correlations between egg diameter and the traits outlined above were estimated, and control line means showed no significant correlation with egg size, with the exception of the positive correlation for larval size at competence. Unexpectedly, phenotypic correlations among selected line means were significantly negative for fecundity, but positive for female dry weight. The positive correlation for larval size at competence also persisted after selection. This may indicate where further work could be useful in examining trade-offs between egg size and other life-history traits.
xi
CHAPTER 1 GENERAL INTRODUCTION The diversity of larval form and function among marine invertebrates has fascinated researchers for decades. Thorson (1950) was among the first to recognize broad-scale patterns in developmental mode and their strong correlation with specific life-history traits (egg size and fecundity). A useful classification of larval types has been based on this observation that numerous marine invertebrates produce high numbers of relatively small, energy-poor eggs, while many others produce fewer, larger, energy-rich eggs. A closely associated dichotomy involves the coexistence of planktotrophic and lecithotrophic larval development. Many marine invertebrates produce pelagic, feeding (planktotrophic) larvae, and these are generally hatched in large numbers from small eggs. Other, often closely related, species produce lecithotrophic larvae that do not depend on exogenous food in order to reach metamorphosis, and these hatch in smaller numbers from larger eggs. Phylogenetic analysis suggests that the transition between these life-history modes has occurred many times (Wray 1996, Duda and Palumbi 1997, Cunningham 1999, Rouse 2000, McEdward and Miner 2001). The adaptive significance of developmental mode has received considerable attention. Selection pressures such as predation, starvation, and dispersal have been proposed for developmental mode evolution (Thorson 1950, Chia 1974, Strathmann 1985), and increases in egg size are often cited as important transitional states between modes (Wray and Raff 1991, Hart 1996, Miner et al. 2005). The suite of characteristics that defines a larval type has not evolved in isolation from post-larval and adult 1
2 characteristics. Egg size and fecundity are two members of a much larger complex of life-history traits that co-evolved, presumably, under the influence of natural selection (Havenhand 1995, Ramirez Llodra 2002). Egg size and fecundity are both directly related to parental fitness (Roff 1992, Bernardo 1996) and many authors have mentioned the importance of interactions between larval characteristics and other parts of the life cycle (e.g., Vance 1973a,b, Christiansen and Fenchel 1979, Todd and Doyle 1981, Strathmann 1985, Moran 1994, Pechenik et al. 1998, Giménez et al. 2004). Few efforts have been made to examine the implications over the entire life cycle of selective pressures on these important and inter-related fitness components. Many studies of marine ecology have used a comparative approach to assess the influence of one life-history stage on another. For instance, maternal environmental conditions influence larval performance in various groups (e.g., Laughlin and French 1989 for the crab Rhithropanopeus harrisii, George 1999 for the seastar Pisaster ochraceus, Qiu and Qian 1997 for the polychaete Hydroides elegans, Giménez and Anger 2003 for the crab Chasmagnathus granulata). Studies have demonstrated that larval experience is linked to juvenile quality (e.g., Jarrett and Pechenik 1997 for the barnacle Semibalanus balanoides, Wendt 1998 for the bryozoan Bugula neritina, Phillips 2002 for the bivalve mollusk Mytilus galloprovincialis, reviewed in Pechenik et al. 1998). Size at hatching affects growth, time to maturity and survivorship in the gastropod Nucella ostrina (Moran and Emlet 2001). Size at settlement influences survival in the ascidian Botrylloides violaceus (Marshall et al. 2006). Hilbish et al. (1993) discussed the common assumption that variation in larval and juvenile growth rates have a common genetic basis, and found that significant genetic variation for larval shell growth in the bivalve
3 Mercenaria mercenaria is not related to the genetic variation in shell growth during the juvenile period. Pechenik et al. (1996) found no correlation of growth rates between larval and juvenile stages in two species of the mollusk Crepidula. Delayed metamorphosis is associated with reduced juvenile or adult performance most often in non-feeding larval forms (e.g., Wendt 1996 for the bryozoan Bugula neritina, Pechenik and Cerulli 1991 for the polychaete Capitella sp. I, Pechenik et al. 1993 for the barnacle Balanus amphitrite, and Maldonado and Young 1999 for the sponge Sigmadocia caerulea). Delaying metamorphosis in the feeding larvae of polychaete Hydroides elegans negatively affects juvenile survival and growth rates whether or not they are fed during the delay (Qian and Pechenik 1998). Delayed metamorphosis in the feeding larvae of the sipunculan Apionsoma misakianum results in reduced juvenile growth whether or not larvae are fed, but does not affect juvenile survival (Pechenik and Rice 2001). Empirical studies have examined the relationship between egg size and larval characters such as rate of development and larval size at metamorphosis in a range of taxa. For example, in opisthobranch mollusks, Havenhand (1993) reports a negative relationship between egg size and development time. Giménez (2002) reports that the crustacean Chasmagnathus granulata hatching from smaller eggs takes longer to develop, as does the seastar Pisaster ochraceus (George 1999). This negative relationship between egg size and development time is also reported for echinoids and asteroids combined (Emlet et al. 1987). Levitan (2000) further refined this relationship by showing that it is negative curvilinear using data from a large group of echinoids. For echinoids and asteroids combined the correlation between size of egg and the size of
4 juvenile at metamorphosis is positive overall (Emlet et al. 1987), but Levitan (2000) shows these two traits to be independent of one another in echinoids, after controlling for phylogeny. Many fewer studies have used an experimental approach to directly manipulate egg size. Sinervo and McEdward (1988) used blastomere separation to show the relationship between reduced parental investment and resulting larval characters in two species of the echinoid Strongylocentrotus. They found that larvae that develop from experimentally reduced zygotes are smaller and take longer to reach metamorphosis than those from whole eggs. Hart (1995) used the same technique and found reduced feeding rates in larvae developing from experimentally reduced zygotes of S. droebachiensis. Emlet and Hoegh-Guldberg (1997) experimentally reduced the lipid content of early zygotes in another urchin, Heliocidaris erythrogramma, and showed a link between reduced parental investment and juvenile performance. Another approach to evaluating the influence of egg size on life history is to examine a single species that shows both developmental modes (poecilogony). Levin et al. (1987) examined the demographic consequences of divergent life-history patterns in a single species of polychaete, Streblospio benedicti, with both planktotrophic and lecithotrophic developmental types. They found that both types achieve similar population growth rates. This overview represents a sample of the diversity of taxa, traits, and methods that have been employed to demonstrate to what extent one stage of life can influence another. Thus, while a large and diverse body of empirical, comparative, and experimental work has demonstrated links between one life-history stage and another, a
5 unified examination of egg, larval, juvenile, and adult traits, and how these correlations influence fitness over the entire life cycle has not been undertaken. As shifts in egg size are often invoked as important transitional states between developmental modes (Wray and Raff 1991, Hart 1996, Miner et al. 2005), and egg size plays a critical role in many of the quantitative modeling approaches that have been used to try and identify selection pressures and processes that influence developmental mode evolution (Vance 1973a,b, Smith and Fretwell 1974, Christiansen and Fenchel 1979, Perron and Carrier 1981, Roughgarden 1989, Podolsky and Strathmann 1996, McEdward 1997, Levitan 2000, Hendry et al. 2001, Luttikhuizen et al. 2004), I focused this study on egg size. Though it is often reported as a fixed parameter, egg size within species displays a large amount of variation (Jaeckle 1995, Hadfield and Strathmann 1996). Considering marine invertebrates, intraspecific variation in mean egg size has been reported for the barnacle Balanus balanoides (Barnes and Barnes 1965). Turner and Lawrence (1979) found significant differences in egg size within species when examining 11 echinoderms, and Lessios (1987) found this same result in a comparison of 13 echinoid species sampled across the Panamanian isthmus. The presence of significant variation in egg size has been reported within species for the starfishes Pteraster tessalatus (McEdward and Coulter 1987), and Solaster stimpsoni (McEdward and Carson 1987), for the polar shrimps Chorismus antarcticus and Notocrangon antarcticus (Clarke 1993), for the dorid nudibranch Adalaria proxima (Jones et al. 1996), for the ascidian Pyura stolonifera (Marshall et al. 2002), and for the euphausiid Thysanoessa raschii (Timofeev 2004). Within and between-species variation in egg size was reviewed for serpulimorph polychaetes by Kupriyanova (2001).
6 Certainly there is abundant phenotypic variation in egg size, but only that portion that has a genetic basis is accessible to selection in order to influence life-history evolution. In order for a trait to respond to natural selection it must have heritable variation, and that variability must have fitness consequences. What component of phenotypic variation in egg size is available to natural selection; what is the heritability of this trait? There is evidence of negative phenotypic trade-offs between fecundity and egg size in unmanipulated populations of a variety of species (Roff 1992). Examples are numerous among arthropods and include crustaceans, lepidopterans, dipterans, and others (Fox and Czesak 2000). The same trade-off has been recorded for treefrogs (Lips 2001); and Sinervo (1990) demonstrated a negative trade-off in phenotypically manipulated lizards. But, there is a limitation to conclusions about evolutionary response to natural selection that can be drawn from phenotypic correlations. If the observed phenotypic trade-off does not represent some underlying genetic antagonism among traits, then it is not revealing the set of options available for selection on these traits. One way to detect this relationship is by using artificial selection experiments that can reveal short-term evolutionary responses for the selected trait. Using both the selection and the manipulation approaches, Schwarzkopf et al. (1999) found no negative genetic correlation between egg size and fecundity in Drosophila melanogaster. Azevedo et al. (1996) also found no evidence for a trade-off between egg size and fecundity in their laboratory-selected lines of D. melanogaster. Blanckenhorn and Heyland (2004) found no evidence of a genetic tradeoff between egg size and number in the yellow dung fly Scathophaga stercoraria. But, in another arthropod, the cladoceran water flea Daphnia,
7 a genetic basis for this trade-off was shown (Lynch 1984, Ebert 1993). Levin et al. (1991) also confirmed a negative genetic correlation between fecundity and egg size in the poecilogonous polychaete Streblospio benedicti, supporting the assumption of trade-offs between these traits. Goals of this study were to investigate the evolvability of the trait of egg size, to examine the direct and correlated responses to selection on increased egg size in a specified set of life-history characters that span the life cycle, and to explore how these correlations change as egg size is increased by artificial selection in the polychaete worm Hydroides elegans Haswell, 1883. Using adult H. elegans collected from the wild, spawned in the laboratory, and raised under common environmental conditions, variation in egg size was documented and heritability for this trait was estimated using a sib analysis (Falconer and Mackay 1996). Using artificial selection for increased egg diameter, realized heritability was estimated (Hill 1972) and the results of selection were documented in a suite of life-history characters as they are reflected through the larval, juvenile, and adult stages. Life-history traits examined included egg diameter, fecundity, and total egg energy (at 6 weeks post-fertilization), larval size at 18 to 20 h post-fertilization, larval size at competence (5 d), tube length at 21 d, and adult dry weight (at 6 weeks post-fertilization).
CHAPTER 2 ESTIMATES OF HERITABILITY FOR EGG SIZE IN THE SERPULID POLYCHAETE Hydroides elegans Introduction Life histories represent compromises between selection on individual fitness components and constraints acting on the organism as an integrated whole. Stearns (1992) suggested that the analysis of life-history strategies must be based on, and consistent with, the evolution of the individual life-history traits. Few individual traits are more fundamental to life history than resource allocation to the egg. Egg size is directly related to parental fitness, and can also have substantial fitness effects for progeny (Roff 1992). Life histories in marine invertebrates are very diverse, and the adaptive significance of developmental mode has received considerable attention. One common feature in the life histories of many invertebrates is an obligate feeding (planktotrophic) larval stage. Paradoxically, it can also often be observed within closely related groups that some members lack this dependence on exogenous food and exhibit lecithotrophic development. It has been hypothesized that nonfeeding larvae evolved as a response to either direct or indirect selection for increased egg size (Jägersten 1972, Strathmann 1978, 1985, Raff 1987, Hart 1996). Selection on egg size has also been linked to developmental mode (Hadfield and Miller 1987), larval development time (Sinervo and McEdward 1988), larval form (Strathmann 2000), size at settlement (Strathmann 1985), survivorship (Bridges and Heppell 1996), and fertilization success (Levitan 2000).
8
9 Vance’s (1973a,b) fecundity-time model regarding the evolution of life histories in marine invertebrates began a series of quantitative modeling efforts focused on egg size as a key trait (Christiansen and Fenchel 1979, Caswell 1981, Perron and Carrier 1981, Grant 1983, Roughgarden 1989, McEdward 1997, Levitan 2000, Luttikhuizen et al. 2004). While the quantitative modeling efforts regarding evolution of life histories in marine invertebrates have become increasingly refined, there has been little research into the genetic architecture of the important trait of egg size in marine invertebrates. In order for a trait to respond to natural selection it must have heritable variation, and that variability must have fitness consequences. Numerous studies have found that egg size typically exhibits phenotypic variability across a wide range of taxa (Hadfield and Strathmann 1996). Phenotypic variation (VP) has several components including the genetic (VG), the environmental (VE), and the interaction between them (VGXE). Unless phenotypic variation represents some underlying genetic variation, it is not heritable and is consequently unavailable to natural (or artificial) selection. VG can be further partitioned; the component that accounts for the resemblance between offspring and parents in sexually reproducing organisms is called additive genetic variance (VA). The proportion of VP that is made up of VA is a quantity called narrow-sense heritability (h2 = VA/ VP). This value is a measure of the resemblance between parents and offspring after sexual recombination and, therefore, is a predictor of short-term response to selection (Falconer and Mackay 1996). Among protostome invertebrates, most of the investigations into h2 of egg size have been focused on the Arthropoda (reviewed by Fox and Czesak 2000): especially the Insecta, a mostly terrestrial group that includes Diptera (flies and mosquitoes),
10 Lepidoptera (moths and butterflies), and Coleoptera (beetles), among others. Many experiments examined egg size in Drosophila melanogaster and demonstrated that there is a significant genetic component to variation for this trait (Warren 1924, Bell et al. 1955, Azevedo et al. 1997, Schwarzkopf et al. 1999). Among lepidopterans, Fischer et al. (2004) estimates h2 for egg size of ca. 0.4 in the butterfly Bicyclus anynana and Harvey (1983) reports h2 for egg weight in the budworm Choristoneura fumiferana at 0.75. Fox (1993) estimates h2 of egg size for the seed beetle Callosobruchus maculatus at 0.43 to 0.59 and 0.60 to 0.74 using two different designs. Czesak and Fox (2003) calculate realized h2 for egg size in the seed beetle Stator limbatus of 0.36 to 0.55. Thus, there is abundant evidence of VA for egg size in insects, and estimates of h2 are generally moderate to large. The only marine invertebrate to receive similar attention was the poecilogonous polychaete Streblospio benedicti, where a reciprocal mating design used to examine the genetic components of life-history traits gave a heritability estimate of 0.75 for egg diameter (Levin et al. 1991). With the exception of this one study on a species with an unusual life history that includes producing both planktotrophic and lecithotrophic larvae, empirical support for theoretical assumptions concerning the heritability of egg size in marine invertebrates has not been examined. The serpulid polychaete Hydroides elegans Haswell, 1883 is an excellent choice as a model organism for estimating h2 for egg size in a marine invertebrate for several reasons. It produces a large number of planktotrophic larvae that can be cultured in the laboratory with relative ease. The larvae will settle and metamorphose in culture in the presence of natural biofilms (Carpizio-Ituarte and Hadfield 1998). The generation time is
11 reasonably short, 16 to 28 days at optimal temperature, salinity, and food concentrations (Qiu and Qian 1998). Both larvae and adult worms can be fed the chrysophyte alga Isochrysis galbana, which is easily cultured in the laboratory. H. elegans develops in the water column with no maternal care. The objective of this study was to obtain estimates of narrow sense heritability for the trait of egg size in Hydroides elegans. I calculated h2 using three different techniques. First, I constructed a half-sib breeding design and used a nested ANOVA for analysis (Falconer and Mackay 1996). Next, Restricted Maximum Likelihood Analysis (Quercus Quantitative Genetics Software, University of Minnesota, USA) was performed on the same data set. Last, artificial selection on egg size was performed and cumulative realized heritability was calculated according to the methods of Hill (1972). Material and Methods Collection and Spawning This project was completed at Kewalo Marine Laboratory, Honolulu, Hawaii using protocols developed there by various workers. Wild worms were collected in November 2002 from Vexar™ screens suspended for 1 month from a floating dock at Ford Island, Pearl Harbor, Hawaii. The sex of each worm was determined and gametes secured by agitation of the calcareous tube surrounding each adult, resulting in release of gametes (Unabia and Hadfield, 1999). Gametes from 270 female worms were used to establish the initial laboratory population. At least 120 males were used, but the exact number of males was not determined. I used a Nikon Coolpix™ 990 camera mounted on an Olympus compound light microscope to obtain digital images of eggs from each female immediately after their
12 release. Mean egg diameter for each mother (n = 10 eggs mother-1) was obtained from these images using NIH Image software. Larval cultures were established at densities of 5 to10 larvae mL-1 in 1L plastic tripour beakers and raised in pooled cultures (4 to 5 mothers and 2 to 3 fathers beaker-1) for Generations 1 through 3. Each beaker had different and unique parents. Cultures were maintained at 25°C, and fed 6 X 104 cells mL-1 day-1of the chrysophyte alga Isochrysis galbana (Tahitian strain). Isochrysis galbana was cultured in the lab at room temperature and constant light, using f/2 media (Guillard 1975) and used during exponential growth phase. All embryos were allowed to hatch in FSW (0.22 µm filtered seawater) and swimming larvae were counted approximately 12 h post-fertiization. At that time larval cultures were established at maximum densities of 10 larvae mL-1 and larvae were fed for the first time. Larvae were fed on Day 2 by adding the appropriate volume of algae to the larval culture beaker without changing water or beakers. On Day 3 and Day 4 larvae were fed and both water and beakers were changed. Day 5 larvae were considered competent to settle and metamorphose. Small transparent plastic chips (2.5 X 1.5 X 0.08 cm; K&S Engineering, Chicago IL, #1306) were placed in flow-through seawater tables for 10 days in order to accumulate natural biofilm, which has been shown to induce settlement in H. elegans (Hadfield et al. 1994). One biofilmed chip was placed in each well of a standard ice cube tray along with 15 mL FSW, I. galbana (6 X 104 cells mL-1), and 20 to 25 competent larvae. Larvae and newly settled juveniles were fed daily at this food density without changing the water for 5 days. This procedure allowed a wide window of opportunity for
13 settlement and avoided inadvertent selection for early settling individuals. Ice trays were kept at room temperature (~24°C) in a Plexiglas™ rack on the bench top with ambient illumination. The position of trays within the rack was randomized daily. On Day 10 (post-fertilization), each chip was removed from the tray and all animals but one were removed. The survivor was determined by position on the chip, with that individual closest to the center selected to be the survivor. Thus, no inadvertent selection for early or late settling individuals, or for body size, took place during this process. At this point, the food level was increased 6-fold (36 X 104 cells mL-1) and worms were fed with the daily water change (FSW) until animals had reached 6 weeks of age. At maturity (here defined as 6 weeks), individual worms were placed in Petri dishes and spawned as before. H. elegans is a protandrous hermaphrodite. Since I was measuring a maternal trait (egg size), I chose a generation time of 6 weeks in order to assure that 50 to 60% of the spawning population would be female. Three generations were so raised under laboratory conditions to minimize variance due to maternal effects. Two hundred or more females were spawned to produce each of these two subsequent generations (217 in Generation 2 and 236 in Generation 3). Within Generation 3 a subset of individual crosses was established to setup the breeding design experiment described below. Alongside the pooled cultures of mixed parentage described above, individual larval cultures consisting only of offspring from a unique mother crossed with a known father were raised under conditions identical to those described above.
14 Half Sib Breeding Design A subset of the worms in Generation 3 was used as parents for the half-sib design experiment (Falconer and Mackay 1996) that was analyzed in Generation 4. Ten males were arbitrarily selected and their sperm was split between two females each (3 females in one case). The result of this mating scheme is to produce offspring related in two different ways, that is, full-siblings (within females, or dams) and half-siblings (within males, or sires). The advantage of this design is to allow the partitioning of the phenotypic variance according to its source (the progeny of different males (σ2SIRE), the progeny of different females mated to the same male (σ2DAM), and individual offspring of the same female (σ2WITHIN). The component of total variance attributable to sires is 1/4 VA, therefore the most straightforward estimate of h2 = 4σ2SIRE/ σ2TOTAL (Falconer and Mackay 1996). Parents and offspring involved in this breeding design were raised in individual and not pooled cultures, but otherwise all conditions were as described above. A fully nested Random Model ANOVA was then used to partition variance in egg diameter according to its source. Type III sums of squares were calculated using the general linear model of SAS Version 6.12 (PROC GLM, with RANDOM statement and TEST option). The variance component data were also used to calculate the additive genetic and residual coefficients of variation (CVA = 100 VA / X and CVR = 100 VP − VA / X , where
X = trait mean) as recommended by Houle (1992). Evolvability is defined as the ability of a trait to respond to selection (Houle 1992) and, using the assumption of directional selection, can be calculated as IA = VA / X 2.
15 I also used Restricted Maximum Likelihood (REML) to analyze these same data, using the nf3 program in Quercus of R.G. Shaw and F.H. Shaw (University of Minnesota, USA; downloaded November, 2004; www.cbs.umn.edu/eeb/events/quercus.shtml). This program estimates the likelihood of observing the data given a set of parameters. Iterative methods are then used to find the set of parameters that maximize this likelihood (Shaw 1987). I used the program to perform REML on a two-generation pedigree with mean egg diameter of each Generation 4 daughter as the single character. The sources of total phenotypic variance were analyzed using the model VP = VA + VD + VE. In this model the genetic variance mentioned above (VG) is partitioned into two components, VA (additive) and VD (dominance). Log likelihood ratio tests were used to compare the fit of the model for significant differences (χ 21) as successive variance components were constrained to zero. Technically, this violates the assumption of the likelihood ratio test because the null value of the parameter (i.e., variance = 0) lies on the boundary of the feasible range. However, the test is believed to be conservative under these conditions (Pinheiro and Bates 2000). Linear regression of mid-offspring egg diameters onto maternal egg diameters was not used because, while each daughter had an independent mother, they were not independent with respect to the father. Therefore, the assumption of independence necessary for the linear regression could not be met. The family based design described here for Generation 4 was repeated in Generations 5 and 6 in an attempt to increase sample size.
16 Selection In Generation 7 the common laboratory population was split into six lines. Three were established as selected lines and three as control lines. Between 12 and 16 females were used to establish each line (Table 2-1). In subsequent generations (Generations 8 to 10), 16 mothers were kept in each line. Within selected lines, the eggs from a specific mother were sub-sampled as described above. Measurements were made immediately and eggs were fertilized only if the mean diameter of the eggs was greater than one phenotypic standard deviation (σP) over the Generation 6 population mean. In subsequent generations, selection proceeded in the same manner, with mothers remaining in the line only if the mean diameter of their eggs exceeded 1 σP over the mean of the selected mothers from the previous generation. If the mothers meeting this criterion happened to include multiple sisters I retained no more than two sisters in a line within a generation. The same rule, that no more than two sisters remain in a line, was also followed for control lines. In control lines, every third or fourth female was fertilized without regard to the size of her eggs. Otherwise, eggs were handled exactly the same as for selected lines. All crosses were between one male and one female with no shared parentage. Males were chosen haphazardly with respect to the mean egg size of the clutch from which they came. Care was taken not to use siblings of either selected or control females as fathers. Larval culture and settlement proceeded as before. Selection continued for four generations (7 through 10). Generally, realized heritability is the change in mean trait value over each generation of selection (offspring mean – parental population mean) divided by the selection differential (trait mean for selected parents – parental population mean). As
17 selection was carried out in one direction only, and the selected and control lines came from the same base population, the realized heritability was calculated according to the specific methods described by Hill (1972). Cumulative realized heritability was calculated as the difference between selected and control values at each generation (Xi) multiplied by the cumulative selection differential for that generation (Si), summed over generations (ΣXiSi). This quantity is divided by the sum over the square of the cumulative selection differential for each generation (ΣSi2). Results Expected mean squares and variance components for the half-sib breeding design in Generation 4 are listed in Table 2-2. Narrow-sense heritability calculated using the sire component of variance (P = 0.069) was h2 = 4σ2SIRE/ σ2TOTAL = 0.45. Confidence intervals were calculated based on the F-distribution, according to Knapp (1986), as recommended for small sample sizes (Hohls 1998). The 95% confidence intervals were large (-0.36 to 0.90) as is often the case for CI for heritability from a breeding design (Koots and Gibson 1996, Markow and Clarke 1997). The mean egg size of Generation 4 daughters used in the nested ANOVA, grouped by mother, was 45.68 µm (± 0.21 µm SE), CVA = 3.22 and CVR = 3.59. Evolvability for the trait of egg size for the Pearl Harbor population of H. elegans was calculated at IA = 10.35 X 10-4. Results from the breeding design experiments in Generations 5 and 6 did not result in an increase in sample size and in both cases the sire component of variance was not significant. Results from the REML analysis on the Generation 4 data were not significant using likelihood ratio tests. The full model (VA, VD, VE unconstrained) gave a negative estimate for VD. Since this is not biologically meaningful, VD was constrained to zero.
18 This produced a result not significantly different than the unconstrained model (χ21 = 0.735; P = 0.45). The estimate of h2 based on this model was VA / (VA +
VE) = 0.38. However, when VA was constrained to zero the log likelihood ratios were still not significantly different (χ21 = 2.519; P = 0.13). Mean egg diameter (µm ± SE) before selection (Generation 6) was 44.78 (0.15), and after selection the mean of the three selected lines was 49.23 (0.35). Direct selection on egg diameter for four generations produced a shift of 4.45 µm or 2.5 σP from the common base population mean (Figure 2-1). Figure 2-2 illustrates the mean egg diameter (µm ± SE) in the base population before selection and among lines after selection began. Egg diameter data for selected Line 1 in Generation 7 were lost due to a corrupted computer file and therefore were not included in calculations of realized heritability. Cumulative realized heritability was calculated using the method of Hill (1972) as 0.58. Bootstrapping based on re-sampling with replacement, and stratified by generation and line, was used to calculate 95% confidence intervals around this estimate. Confidence intervals based on 1000 replicates were 0.51 to 0.66. Discussion There has been considerable interest in the evolution of life histories in marine invertebrates, and egg size has played a critical role in many of the quantitative modeling approaches that have been used to try to identify selection pressures and processes that influence the evolution of developmental mode in this group. In order for evolution to occur, some component of phenotypic variation in egg size must be additive genetic variation. My objective was to determine if the assumption of many models, that egg size can and does respond to selection, is reasonable by estimating h2 for a marine
19 invertebrate with a wide geographic range, small egg, and obligate planktotrophic larvae. All estimates of heritability carry the constraint that they only apply to the population measured under those environmental conditions and are not specifically applicable to other populations (Falconer and Mackay 1996). I have shown that there is significant additive genetic variation for egg size in the Pearl Harbor population of H. elegans using various analytical techniques. The response of 2.5 σP to direct selection on egg size indicates that there is substantial potential for egg size to respond to varying selective pressures, at least in the direction of an increase. It is apparent in Figure 2-2 that variation within selected lines was not reduced relative to either values before selection, or to control lines. In a half-sib breeding design, offspring have one parent in common and the other parent different. The degree of resemblance among half-sibs (the covariance of half-sibs) represents half the variance of the common parent or a quarter of the additive genetic variance (Falconer and Mackay 1996). The estimate of heritability reported here (0.45) was based on the sire component of variance. One of the advantages of using the sire component for this estimate is that it does not include maternal or dominance effects (Falconer and Mackay 1996). It is possible to use this breeding design to estimate these effects by examining the variance within dams (σ2DAM), since it includes both maternal (common environment) and dominance effects, and comparing it to the estimate based on the sire component. However, since my estimate of σ2DAM was not statistically significant (P = 0.667), and the proportion of VP explained by this estimate was essentially zero (Table 2-2), further extrapolation based on this estimate cannot provide useful information. Maternal effects are widely recognized as important components of
20
Vp (Mousseau and Fox 1998), although this is more common in mammals and animals with longer periods of maternal care. Hydroides elegans has external fertilization. All development up to a competent larva takes place in the water column and there is no evidence of parental care. However, it is possible that the small sample size in my breeding design (10 sires, 21 dams) resulted in an overestimate of σ2SIRE, obscuring my ability to detect σ2DAM and estimate maternal effects. Therefore, based on these data, I cannot say whether maternal effects are contributing significantly to the total phenotypic variance. Cumulative realized heritability is considered the most precise of the various methods for determining narrow-sense heritability (Hill 1971). The cumulative realized heritability estimate does include maternal effects, since it is based on response to selection, but passing six generations under laboratory conditions prior to the beginning of selection minimized the phenotypic expression of any maternal effects. The half-sib breeding design gave only a slightly lower estimate of h2 (0.45) compared to the cumulative realized heritability (0.58). The fact that two estimates are similar lends some support to the idea that maternal and dominance effects are not large in this population with respect to this trait. It is thought that additive genetic variation for traits closely related to fitness, such as egg size, should be under constant directional selection, eroding VA and resulting in low heritabilities (Gustafsson 1986, Roff and Mousseau 1987, Falconer and Mackay 1996). This trend is generally supported for life-history traits as compared to morphological traits (Mousseau and Roff 1987). However, many exceptions can be found (e.g., Levin et al. 1991, Gibson 1993, Fox and Csezak 2000, Edmands 2003),
21 including this work. Houle (1992) pointed out that because h2 is a ratio of VA to VP, the magnitude of VP greatly influences the outcome: low h2 could be the result of low VA or high VP. Therefore, it is a biased estimate of additive genetic variance and potentially a misleading indicator of the ability of a particular trait to respond to selection. Using coefficients of variation, that is VA standardized by the trait mean rather than VP, is recommended as a more useful approach. My estimates of CVA and CVR give very similar values (3.22 and 3.59 respectively) implying that nearly half of the total variation present is additive genetic. This is consistent with my estimate of h2. Using the traditional methods of estimating h2, and also by calculating CVA and IA, I have found significant levels of additive genetic variance for the trait of egg size in the Pearl Harbor population of H. elegans. Several hypotheses have been offered to explain the apparent paradox of finding VA for a life-history trait that is closely linked to fitness and, presumably, under directional selection. One such hypothesis is the presence of microevolutionary trade-offs. Microevolutionary trade-offs occur when a change in one trait that acts to increase fitness is linked to a change in another trait that decreases fitness (Stearns 1992). These relationships can act to constrain the simultaneous evolution of suites of fitness-related traits and thereby maintain additive genetic variance in a population. Examination of the correlated responses of other fitness-related traits to artificial selection for increased egg size is one way to elucidate this relationship. Table 2-1. Number of females used to establish six individual lines in Generation 7 Line Number of Females 1 12 2 12 3 15 4 15 5 16 6 16
22 Table 2-2. Half-sib breeding design; Fully nested ANOVA and variance component analysis for egg diameter in Hydroides elegans (number of observations 550, s = 10, d = 2.1, k = 2.6) Source df EMS Proportion F P VP explained (X 10-5) Sire 9 4.149 16.54 0.069 11.13 Dam (Sire) 11 1.575 6.28 0.667 0 Daughter (Dam (Sire)) 34 2.047 8.16 0.0001 37.11 Error 495 0.251 --51.75
45 Generation 6
40
Generation 11
35 30 25 20 15 10 5 0 40 41 42 43
44 45 46 47 48 49 50 51
52 53 54 55
Egg diameter (µm)
Figure 2-1. Response to direct selection on egg diameter for four generations of in the polychaete Hydroides elegans. Selection began from a common base population in Generation 6 and continued from Generation 7 through 10
51
Selected Line 1 Selected Line 3 Selected Line 5 Controls Line 2 Controls Line 4 Controls Line 6 Common Population
50 49 48 47 46
23
45 44 43 Gen 3
Gen 4
Gen 5
Gen 6
Gen 7
Gen 8
Gen 9
Gen 10
Gen 11
Generation
Figure 2-2. Mean egg diameter (± SE) before and after direct selection for increased egg diameter in replicate selected (1,3,5) and control (2,4,6) lines of Hydroides elegans
CHAPTER 3 DIRECT AND INDIRECT RESULTS OF ARTIFICIAL SELECTION FOR INCREASED EGG SIZE IN THE SERPULID POLYCHAETE Hydroides elegans Introduction Marine invertebrates exhibit a wide diversity of developmental strategies and their mode of development is thought to have important effects on dispersal and population structure (e.g., Hedgecock 1982, Levin and Huggett 1990, McMillian et al. 1992, Hoskin 1997, Collin 2001), geographic range (Scheltema 1989, Kohn and Perron 1994, but see Emlet 1995), and rates of speciation and extinction (Strathmann 1985, Jablonski 1986, 1987). Egg size has been the focus of a series of quantitative modeling efforts to analytically assess the patterns we observe in marine invertebrate life histories. Beginning with Vance’s influential fecundity-time model (Vance 1973a,b), numerous authors have examined trade-offs between egg size, fecundity, mortality and their relationship with the evolution of different reproductive strategies (Christiansen and Fenchel 1979, Caswell 1981, Perron and Carrier 1981, Grant 1983, Roughgarden 1989, McEdward 1997, Levitan 2000). Another set of models examines fertilization kinetics, which also can pose selective pressures on egg size and thus developmental mode (Levitan 1993, 1996, Luttikjizen 2004). Many authors have emphasized that the suite of characteristics that defines a larval type has evolved in conjunction with post-larval and adult characteristics, rather than in isolation. Egg size and fecundity are two members of a much larger complex of life-history traits that has co-evolved, presumably under the influence of natural selection 24
25 (Havenhand 1995, Ramirez Llodra 2002). Egg size and fecundity are both directly related to parental fitness (Roff 1992, Bernardo 1996) and many authors have mentioned the importance of interactions between larval characteristics and other parts of the life cycle (e.g., Vance 1973a,b, Christiansen and Fenchel 1979, Todd and Doyle 1981, Strathmann 1985, Moran 1994, Pechenik et al. 1998, Giménez et al. 2004). Few efforts have been made to examine the implications over the entire life cycle of selective pressures on these important and inter-related fitness components. Much of life history theory is based on the assumption of trade-offs among traits that contribute to fitness, that is, that natural selection cannot produce unlimited simultaneous increases in individual fitness components. This could result in creating theoretical optima based on trade-offs between fitness components (Roff 1992, Stearns 1992). Fitness components, and therefore trade-offs between them, must have a genetic basis for selection to act. Alleles that increase fitness without a cost are expected to achieve a frequency of one very quickly; therefore genetic correlations between fitness-related traits that have been subject to simultaneous selection are expected to become negative. Several methods are in use to examine the genetic architecture of fitness-related traits. Genetic correlations may be estimated by examining the resemblance between relatives using designs similar to those for estimating heritabilities (Falconer and Mackay 1996, Lynch and Walsh 1998). These correlations are caused by pleiotropy, where traits of interest are influenced by common genes; however, they may also be caused by linkage disequilibrium between distinct loci, each influencing a different trait. But genetic correlations between life-history traits can be difficult to extrapolate from
26 breeding designs. Correlations estimated in this manner are dependent on linkage equilibrium and other requirements (Rose et al. 1990), and standard errors around these estimates are often very large (Koots and Gibson 1996). A second, and more direct method that can be used to look for evidence of evolutionary trade-offs is artificial selection. Artificial selection experiments allow workers to manipulate the frequency of alleles associated with a phenotypic value of a selected character by controlling the parental genetic contribution to the next generation in laboratory populations, thereby producing divergent phenotypes. If selected lines differ from control lines in traits other than the selected trait (and environmental variation has been kept constant across generations), this response indicates an additive genetic correlation between the traits (Cheverud 1984). Repeated episodes of selection over multiple generations are more likely to reveal potential interactions between fitness components that may be subtle or difficult to measure across a single generation. Artificial selection experiments are a particularly powerful way to explore trade-offs (Reznick 1985, 2000, Brakefield 2003). However, selection experiments are subject to experimental or procedural artifacts that may be difficult to control, and the complexity and interactive nature of response to selection can produce varying outcomes (Harshman and Hoffman 2000). Selection experiments on life-history traits have a long history, with the preponderance of work in invertebrates involving insects. For example, Englert and Bell (1969, 1970) selected on larval development time in the flour beetle Tribolium
casteneum, Roff (1990) selected on wing dimorphism (an indicator of development time) in the sand cricket Gryllus firmus, Bradshaw and Holzapfel (1996) selected on
27 development time in the pitcher-plant mosquito Wyeomyia smithii, and Palmer and Dingle (1986) selected on wing length (an indicator of dispersal ability) in the milkweed bug Oncopeltus fasciatus. Focusing on correlated responses in egg size, Tucic et al. (1998) and Seslija and Tucic (2003) found that bean weevils, Acanthoscelides obtectus, selected for faster development times lay significantly larger eggs. A similar correlated response in egg size to selection on development time is reported for Drosophila
melanogaster by Bakker (1969). Selection experiments involving life-history traits in D. melanogaster are numerous, especially focusing on trade-off between longevity, fecundity, and larval development time (e.g., Tantawy and El-Helw 1966, Partridge and Fowler 1992, Zwaan et al. 1995, Nunney 1996). Several studies have examined response to selection on egg size. A significant response to selection toward both large and small eggs has been reported in Drosophila
melanogaster in several studies (Bell et al. 1955, Parsons 1964, Schwarzkopf et al. 1999). Azevedo et al. (1997) found evidence of a selective advantage to larger eggs in D.
melanogaster, including increased embryonic viability, hatchling weight, and larval and pre-adult development rates. Czesak and Fox (2003) selected directly on egg size in the seed beetle Stator limbatus and report correlated responses in lifetime fecundity and female body mass. Among marine invertebrates genetic correlations for selected life-history characters have been reported using breeding designs. In mollusks, Ernande et al. (2003) report a positive correlation between reproductive plasticity, growth and survival for the bivalve
Crassostrea gigas. Hilbish et al. (1993) discuss the common assumption that variation in larval and juvenile growth rates have a common genetic basis, but find no significant
28 correlation between variation for larval and juvenile shell growth in the bivalve
Mercenaria mercenaria. Gibson (1993) explored genetic correlations among life-history traits in the poecilogonous opisthobranch Haminoea callidegenita and found that many reproductive traits showed significant genetic correlations while exhibiting little or no phenotypic correlations. In crustaceans, Arcos et al. (2004) estimate the genetic basis for a series of reproductive traits in the white shrimp Penaeus vannamei and report no correlation between egg diameter and other traits, but did find a positive correlation between egg number and egg total protein. Levin et al. (1991) investigated the genetic architecture of the poecilogonous polychaete Streblospio bendicti using a diallel design and confirmed a negative genetic correlation between egg size and fecundity, as well as the expected positive genetic correlation between fecundity and female body size. Ernande et al. (2004) used a nested half-sib mating design to examine five traits in
Crassostrea gigas: larval shell length, size at settlement, weight after metamorphosis, juvenile weight, adult weight, but did not examine egg size. They report that larval development rate is positively genetically correlated with size at settlement, but negatively correlated with both metamorphic success and juvenile survival. Little work has been done to examine the consequences across the life cycle of shifts in egg size. The purpose of this work was to examine the direct and correlated results of artificial selection to increase egg size in Hydroides elegans Haswell, 1883. H. elegans is a marine, serpulid polychaete worm that produces numerous planktotrophic larvae and can be cultured in the laboratory over multiple generations. Larvae will readily settle and metamorphose in culture in the presence of natural biofilms (Carpizio-Ituarte and Hadfield 1998). Fertilization and larval development takes place in the water column
29 with no maternal care and H. elegans develops as a protandrous hermaphrodite (Ranzoli 1962). The generation time is 16 to 28 days at optimal temperature, salinity, and food concentrations (Qiu and Qian 1998). Both larvae and adult worms can be fed the chrysophyte alga Isochrysis galbana, easily cultured in the laboratory. Using artificial selection for increased egg diameter, correlated responses were documented in a suite of life-history characters: egg diameter, fecundity, total egg energy (at 6 weeks post-fertilization), larval size at 18 to 20 h post-fertilization, and at competence (5 d), juvenile tube length at 21 d, and adult dry weight (at 6 weeks). Methods Collection, Spawning, and Selection Wild Hydroides elegans were collected at Ford Island, Pearl Harbor, Hawaii in November 2002. Details of the methods for spawning, larval culture, measurement of egg diameter and selection are described in detail in Chapter 2. Field collected worms were raised under controlled environmental conditions for six generations before selection began in Generation 7. Between 12 and 16 females were used to establish each line in Generation 7 (Table 2-1). In subsequent generations (Generations 8 to 10), 16 mothers were kept in each line. All crosses were unique and the fathers were chosen haphazardly without regard to the mean egg size of the clutch from which they hatched. No crosses were permitted between brothers and sisters within lines. Three replicate control and three replicate selected lines were established with 128 worms in each line, for a total of ~768 worms in each generation. All females were spawned at 6 weeks post-fertilization and females were retained in the selected lines if the mean diameter of their eggs was ≥ 1σ than that of the previous generation. For control lines, every third female spawned was retained in without regard to egg diameter.
30 Larval culture was performed according to methods described by Unabia and Hadfield (1999). Cultures were maintained at 25°C, and fed 6 X 104 cells mL-1 day-1of the chrysophyte alga Isochrysis galbana (Tahitian strain). Larvae were competent to metamorphose at 5 d post-fertilization, when I exposed 20 to 25 larvae to individual small plastic chips with natural biofilm as the settlement cue. Each chip was isolated in a single well of a standard ice cube tray filled with 15 mL of 0.22µm filtered seawater (FSW) and algal food was maintained at 6 X 104 cells mL-1 day-1. On Day 10 all juveniles but the one nearest the center of the chip were killed by destroying the tube, so that growth from that point took place at a density of 1 worm well-1. Food density was increased 6-fold and water, food, and container (ice tray) were all changed daily until adults were spawned. I observed that some female worms in both selected and control lines spontaneously released a few eggs (from 10 to a few hundred eggs) shortly after the daily food and water change. I collected all the early-spawned eggs that were produced after the daily food and water change over a four- day period (October 10 to 14 2003) prior to the scheduled spawning of Generation 9 using a Pasteur pipet. There were 25 selected and 7 control females (n = 32 females) that produced early-spawned eggs over this four-day period. I began the scheduled spawning of these same females two days later. Therefore, the timing of the sample of early-spawned eggs ranged 6 to 12 d prior to the scheduled spawning date for these individuals. I used digital imagery (Chapter 2) to measure mean egg diameter of these early-spawned eggs (n = 10 eggs female-1) and compared this to mean egg d measured at the time of induced spawning (later-spawned eggs) of the same female.
31 Selection continued for four generations with lines terminated at Generation 11, when adult dry weight, total egg energy, fecundity and final egg diameter were determined. Larval size at two different time points, and juvenile tube length were measured in Generation 10, as no larvae or juveniles were available after termination of the lines. Larval Size At 18 to 20 h post-fertilization sub-samples of trochophore-stage larvae were taken from nearly all of the crosses (between 11 and 16 of the 16 crosses in each line) in Generation 10. Any crosses for which I had not obtained video by the time they had developed to 20 h were not sampled. Larvae from a single cross were placed on a clean slide and excess water was removed with a micropipette. A cover slip was placed on each slide using Scotch™ tape to elevate the slip above the slide. Using a technique similar to that used by Leonardos and Lucas (2000) for bivalve larvae, videotapes of the swimming larvae were obtained using a Sony Digital Video Camera Recorder (Model DCR-TRV30) mounted on an Olympus light microscope. A stage micrometer was used as a scale for each series of shots. Videos were downloaded to a Macintosh G4 where iMovie software was used to grab still photos of larvae (n = 10 larvae cross-1). NIH Image software was used to measure the width across the prototroch, and the distances from the prototroch to the apex of the episphere and hyposphere, respectively. Larval size was then calculated as the volume of two circular cones (V = π r2h/3; r = 1/2 prototroch width and h = distance to apex of episphere or hyposphere). The same process was repeated for competent larvae at 5 d post-fertilization, including between 9 and 15 of the 16 crosses in each line (n = 10 larvae cross-1) in Generation 10.
32 Juvenile Tube Length Shortly after metamorphosis a calcareous tube is constructed by the juvenile. The tube lengthens as the worm grows, and tube length is a reasonably reliable indicator of juvenile size (Qian and Pechenik 1998, Qiu and Qian 1998). This indirect method of measuring juvenile size was chosen to minimize loss of individuals from laboratory lines, since removal from the tube results in death. Images of juvenile tubes at 21 d were obtained using the Nikon Coolpix™ 990 described above, attached to an Olympus dissecting microscope. Each individual chip was removed from the ice tray and placed in a plastic Petri dish along with a 1cm length of ruler. Images were obtained for all offspring (n = 8 juveniles cross-1) from between 10 and 16 crosses from each line in Generation 10. The images were analyzed for tube length using NIH Image software. Total Egg Energy In Generation 11 each sub-sample that had been used to measure egg diameter was placed in a cryotube (FisherBrand 0.5 mL screw-top tube) and frozen at -20°C. Frozen samples from each line were later analyzed for organic content using a micro-modification of the dichromate oxidation technique (Jarrett and Pechenik 1997, Gosselin and Qian 1999) against a glucose standard (0 to 20 µg C). Eggs were thawed at room temperature and distilled water was added to raise the volume to 200 µL. Four replicate sub-samples of 10 µL were obtained and counted on a Petri dish using a dissecting microscope and a hand-counter. This allowed calculation of the total number in the sample that was needed to complete the fecundity estimate (see below). The counted samples were removed from the Petri dish using a micropipette and placed in a 13mm glass test tube. Between 300 and 500 eggs were placed in each of
33 three replicate tubes from a particular cross. Sixteen samples, each corresponding to a different randomly selected cross from each line, were prepared. Tubes were allowed to stand until the eggs had settled to the bottom and excess water was removed using a micropipette. The eggs were incubated in 1 mL concentrated (85.5%) phosphoric acid (15 min at 105°C) to remove excess chloride. Tubes were cooled to room temperature and 1 mL of 0.04% acid dichromate was added to each tube to oxidize the sample. Tubes were mixed on a vortex mixer followed by incubation at 105°C for 15 min. Reduction in dichromate concentration indicates the amount of organic carbon oxidized. Samples were diluted by adding 5 mL distilled water followed by vortex mixing. A 0.5 mL aliquot was removed from each tube and combined with 4.5 mL of cadmium iodide starch reagent (Parsons et al. 1984) and allowed to stand at room temperature for 20 min. Each sample was then diluted again by adding 5 mL distilled water and examined spectrophotometrically (Kontron Instruments, Model Uvikon 930) at 575 nm. Total energy was estimated as µg C equivalents in glucose and converted to mJ using the relationship 1 µg C = 39 mJ (McEdward and Carson 1987). Though widely used in comparative studies of egg energy in marine invertebrates, the dichromate oxidation technique is known to underestimate energy contributed by proteins (Gosselin and Qian 1999). Pernet and Jaeckle (2004) analyzed this technique across species within annelids and echinoderms and conclude that the likely cause is that different proteins oxidize to different degrees in the acid dichromate reaction. Their comparison points out that across a wide range of species, developmental modes, and egg sizes there is probably a wide range of differential allocation of various proteins and
34 because of this the absolute value of energy egg-1 may be underestimated using this assay. Here I used the acid dichromate technique for a relative comparison of mean total energy egg-1 within species, over a small range of egg sizes after short-term selection. Data presented by Pernet and Jaeckle (2004) for planktotrophic annelids show that error of total energy estimates based on this technique within species is generally small (e.g., estimates for serpulid polychaetes include Serpula columbiana with 0.65 mJ egg–1 ± 0.015 SE, or 2.3% and Hydroides sanctaecrucis with 0.40 mJ egg–1 ± 0.023 SE, or 5.8%) and therefore unlikely to be important over the small changes in egg size considered here. There are two possible ways that an increase in error could affect my results. First, in the unlikely event that short-term selection on egg size resulted in a change in the type of protein allocated to eggs of selected lines relative to control lines, error could be increased. Second, if selection produced increased densities of a particular protein in larger eggs, this could affect the error. Either of these would be an interesting outcome and should be considered by future workers using techniques specific to these questions. Absolute values of energy estimates based on this technique may be underestimates. Fecundity In Generation 11, after the sub-sample of eggs for measurement and total energy oxidation were removed, the remaining eggs from each female (n = 435) were fixed in 5% formalin in FSW (~2% formaldehyde). These samples were set aside and eggs were counted later. The samples were diluted to 30 mL using filtered seawater and a standard 50 mL graduated cylinder. The sample was mixed by inversion and 4 sub-samples of 250 µL each were placed on a Petri dish and counted using a dissecting scope and a hand counter. The number of eggs in the fixed sample was then calculated. The number of
35 eggs from the frozen samples (see above) was added to this number to obtain the absolute number of eggs produced by each female. The relative fecundity was also calculated by dividing the absolute number of eggs per female by her dry weight (see below) to give eggs mg-1. Adult Dry Weight The dry weight of each adult in Generation 11 (n = 685) was determined. Small squares of aluminum foil were numbered and pre-tared on a Cahn (Model C-35) micro-balance. Immediately after spawning sex of the worm was recorded, and each individual was removed from the calcareous tube using forceps to crack the tube. Worms were rinsed in distilled water and placed on aluminum foil squares. Specimens were placed in a drying oven at 75°C for 48 h. Worms were re-weighed on the Cahn balance to the nearest 0.1 µg and the weight of the foil was subtracted providing a post-spawn weight for each individual. Data Analysis I used a fully nested mixed model ANOVA with fixed effects at the level of treatment only with lines nested within treatments and crosses nested within lines for the traits egg diameter, total egg energy, larval sizes at 18 to 20 h and at 5 d, and juvenile tube length (all nested at all levels between selected and control lines). Data were visually checked for radical departures from normality and heteroscedasticity and none were found. For the analysis of adult dry weight and fecundity the same fully nested mixed model ANOVA was used with fixed effects at the level of treatment only and lines nested within treatments. In order to test for an effect of selection on the relative numbers of males and females across generations I used a model I ANOVA. In all cases
36 Type III sums of squares were calculated using the general linear model of SAS Version 6.12 (PROC GLM, with RANDOM statement and TEST option), α = 0.05 unless otherwise stated. To compare mean egg d between early- and later-spawned eggs within mothers I used a paired t-test in JMP 5.1 (SAS Institute, Inc.). Results Direct Response to Selection Mean egg diameter in the base population (Generation 6) was 44.78µm (± 0.15 SE); the mean egg diameter in the selected lines after selection (Generation 11) was 49.23µm (±0.35 SE). Direct selection for four generations for increased egg size resulted in a shift of 4.45 µm or 2.5 σP from the common base population mean (Figures 2-1, 2-2). Figure 3-1 illustrates the continued positive slope of the cumulative response to selection through Generation 11 as the difference between the mean egg diameter of the replicate selected and control lines. Egg diameters between selected and control lines were significantly different at Generation 11 (P = 0.0006, Table 3-1). Correlated Responses to Selection Replicate lines selected for larger egg diameter were found to have a significantly higher mean value for total energy relative to the control lines (P = 0.0350, Table 3-2). The mean value (mJ egg-1 ± SE) for the selected lines was 0.37 (0.17) and for the control lines the mean was 0.29 (0.18). Fecundity, calculated as the absolute number of eggs produced by a female (± SE), was significantly higher in the large-egg selected lines relative to controls (P = 0.0304, Table 3-3). Female worms in the large-egg lines produced a mean of 10071 (481) eggs and females in control lines produced a mean of 7936 (418). When egg number was
37 standardized by the dry weight of the mother to give eggs mg-1 the difference between the selected and control line means became less apparent, significant at α = 0.10 (P = 0.0679, Table 3-4). Both of these analyses were also performed on datasets omitting all mothers that had produced eggs prior to the induced spawning at 6 weeks (see Spontaneous Spawning below) and the outcome was not changed. No significant difference was found in the dry weight of adult females from selected lines relative to control lines (P = 0.6567, Table 3-5). The mean dry weight (mg ± SE) for females in the selected lines was 0.80 (0.019) and for controls was 0.82 (0.026). The same result was found if males and females were combined within treatments (P = 0.5791), and for males alone (P = 0.8526). The Generation 11 mean dry weight of adults of both sexes from the selected lines was 0.81 (0.025) and from the control lines this value was 0.83 (0.020). Males could not be distinguished from females on the basis of dry weight within either the control (P = 0.1974) or selected (P = 0.1698) lines. No significant difference was detected in larval size (volume) at 18 to 20 h between selected and control lines (P = 0.3392, Table 3-6). The mean value for larval size (µL ± SE) at 18 to 20 h for the large-egg selected lines was 1.12 X10-4 (0.064 X 10-4). The control lines had a mean value of 1.14 X10-4 (0.047 X 10-4). Larval size (volume) at competence was significantly larger in the selected than in the control lines at α = 0.10 (P = 0.0894, Table 3-7). The mean size at competence in the selected lines size (µL ± SE) was 1.29 X 10-3 (0.041 X 10-3) and for the control lines it was 1.16 X 10-3 (0.036 X 10-3).
38 Selected lines did not significantly differ from control lines in tube length at 21 d (P = 0.1249, Table 3-8). Mean tube length (mm ± SE) was 8.08 (0.31) in the selected lines and 8.60 (0.10) in the control lines. Direct and correlated responses to selection for increasing egg diameter are summarized in Table 3-9. Spontaneous Spawning and Sex Ratios In an effort to explore the relationship between egg diameter and time of spawning, I compared the mean egg diameter from spontaneously or early-spawned females to that of eggs produced at 6 weeks by the same female (n = 32) in Generation 9. The later-spawned eggs were significantly larger than the early-spawned within individual mothers (paired t-test, t = 9.8582, P < 0.0001). In an unexpected development, I observed that females in the selected lines tended to spawn spontaneously more frequently and earlier than control females. Timing and frequency of these events was not recorded since it was not part of the experimental design. Within this design I controlled the absolute age of individuals at spawning (6 weeks), but not the time to sex change. At 6 weeks an individual female might have been producing eggs for variable periods of time. Considering that within mothers later-spawned eggs are significantly larger than earlier-spawned eggs, was it possible that large-egg selected mothers had been producing eggs longer than control mothers? If selected lines were changing sex earlier than control lines, one prediction would be a higher proportion of females in selected lines relative to controls at 6 weeks. Since the sex of each individual was recorded at the time of spawning for all generations I was able to document an effect of selection on sex ratios, showing that the proportion of females at
39 6 weeks increased in the selected lines, relative to controls, across Generations 7 through 11 (P = 0.0122, Table 3-10). The mean percentage of females in selected lines ranged from 64.70% to 74.30% and for control lines the range was 59.21% to 64.21% (Table 3-11).
H. elegans has been described as a sequential hermaphrodite in all accounts since Ranzoli (1962) clarified their status as hermaphrodites, and I also found this condition in all control lines (as well as in thousands of individuals raised under laboratory conditions prior to selection). However, in all 3 replicate selected lines on at least one occasion I observed simultaneous eggs and sperm being produced by the same individual (again, spawned at 6 weeks). Discussion More + Bigger = Better… or Does It? I predicted that there would be negative correlations between at least some fitness related traits, because we expect alleles underlying advantageous genetic correlations to be rapidly fixed in natural populations. Yet I found that large-egg selected females produced more eggs, with higher energy content, that grew into larger larvae at competence. Increased size at settlement is considered a selective advantage (reviewed by Pechenik 1999). No trade-off with this apparently advantageous condition (the production of more energy-rich eggs that grow into larger competent larvae) was immediately evident by evaluating the initial traits of interest. This set of apparently advantageous correlated traits raises the question what other traits offset the selective advantage of larger egg size in natural populations? One of the advantages of using a selection experiment to explore evolutionary processes is that correlated responses to selection can reveal unexpected relationships
40 between traits that were not predicted at the start of the experiment (Harshman and Hoffman 2000). The observation that selected worms appeared to produce eggs spontaneously both earlier and more frequently than control lines prompted me to examine the relative numbers of males and females across generations and I found that direct selection for increased egg diameter produced significantly higher proportion of females at 6 weeks of age. Considering that I also found that egg diameters are significantly larger in females that spawn later than those that spawn earlier, I propose that selection for increased egg size was manifest through selection for earlier sex change. This earlier sex change resulted in selected individuals spending less time as males relative to controls, consequently reducing the number of offspring they could potentially father. Sex allocation theory predicts that sex change (sequential hermaphroditism) is favored when an individual experiences differential reproductive success in relation to size (or age). According to the size-advantage hypothesis selection should favor protandry if male reproductive success does not increase as individuals grow larger, while female reproductive success does (Ghiselin1969). There has been broad empirical support for this hypothesis (e.g., Charnov 1979a for the protandrous shrimp Pandalus, Warner 1984a,b for protogynous coral reef fishes, Berglund 1990 for the protandrous polychaete Ophryotrocha puerilis). The optimal timing of sex change within individuals is also predicted by the model (Charnov 1979b, 1982). Sex change should theoretically occur when an individual’s reproductive value (future expectation of reproductive success weighted by the probability of survival) as a member of its present sex declines below the reproductive value of the opposite sex. Alterations between male versus
41 female investment should only be favored if the gain in reproductive value in one sex exceeds the loss in the other sex (Leigh et al. 1976). An individual should change sex if it can increase its lifetime reproductive value by doing so, and should change at that point where the sum of the male and female components is maximized. The earlier sex change that resulted as a correlated response to selection in H. elegans could reduce the contribution of the male component to lifetime reproductive value to such an extent that the female component cannot compensate for the loss. This assumes that males are not able to shift their own sexual maturity earlier, or at least not sufficiently earlier to make up for the loss in reproductive fitness resulting from terminating sperm production earlier. Earlier sex change could occur as a result of male and female gametogenic processes being controlled by different and unlinked genes, that is, a response that shifts the timing of investment in oogenesis manipulates a different suite of genes entirely than those that control the timing of spermatogenesis. It is likely that the spermatogenic pathway has already been selected to function at the earliest possible age, and therefore smallest size, because H. elegans is an opportunistic polychaete, and among the first settlers into disturbed environments. Maternal biosynthesis, mobilization and bioaccumulation of nutrients during oogenesis is an energy intensive activity and it is reasonable to assume that there is a cost involved in pushing this activity to an earlier time in the life cycle until it nearly, or actually, overlaps with sperm production. Therefore, I propose that the constraint on increased egg diameter (at 6 weeks) in this population is selective pressure to maintain the optimum male contribution to lifetime reproduction. One question that follows on this reasoning is, if it is costly to change sex early, then how is variation for the trait of “time to female” maintained in the population?
42 One possible explanation is frequency-dependent selection, that it is very profitable to be an early sex-changing female when the trait is rare (and everyone else is male), but becomes less profitable, even costly, as the frequency increases. Though it is widely reported that sequential hermaphrodites change sex as their size increases, field studies commonly report extensive overlap between male and female size classes (Wright 1989, Sewell 1994, Collin 1995). Ranzoli (1962) surveyed field populations of H. elegans (as H. norvegica) over a three year period using segment number as an indicator of size and also found considerable overlap between the sexes. Population studies necessarily include overlapping generations; however, even with the discrete generations raised here I observed no significant difference in somatic dry weight between the sexes. This variation in size at 6 weeks may indicate significant genetic variation in maximum body size, or possibly in growth rate in this population. Many of the males that remained in both selected and control lines at 6 weeks were quite large and the mean dry weight for males was larger (although not significantly so) in both treatments. Given the positive correlation between egg size and egg number reported here, one may ask how often, and under what conditions the predicted trade-off between egg size and egg number has been empirically demonstrated. Varying environmental conditions can result in an interaction between genotype and environment (G X E) and reveal a trade-off. Czesak and Fox (2003) found that the magnitude of the trade-off between egg size and fecundity varied between environments in the seed beetle Stator limbatus. Varying food levels revealed a trade-off between increased fecundity and mortality in the polychaete Dinophiilus gyrociliatus (Prevedelli and Zunarelli Vandini 1999, Prevedelli
43 and Simonini 2000). Tatar et al. (1993) nicely demonstrate the trade-off between increased egg production and increased age-specific mortality in the beetle
Callosobruchus maculatus. A longstanding idea concerning the evolution of offspring number is the “Lack clutch size” hypothesis in birds, that is, that clutch size has evolved towards the size that will maximize the number of successful fledglings. Empirical tests of the “Lack clutch”, and deviations from it, continue to produce mixed results. For example VanderWerf (1992) used meta-analysis on data from 77 different ornithological studies and found that the hypothesis was not supported. Frequently cited examples of the egg size-egg number trade-off in marine invertebrates are poecilogonous species such as the polychaetes Streblospio benedicti (Levin and Creed 1986, Levin et al. 1987) and
Capitella sp. (Qian and Chia 1991) that have sympatric populations capable of producing either planktotrophic or lecithotrophic larvae. The reproductive output of both strategies is similar but lecithotrophs produce fewer, larger eggs while planktotrophic populations produce smaller, more numerous eggs. The negative genetic correlation between egg size and fecundity was confirmed for Streblospio benedicti by Levin et al. (1991). However, poecilogony is an extremely unusual developmental strategy (Hoagland and Robertson 1988, Bouchet 1989) and may not represent a general pattern. In examining the more typical reproductive strategies the genetic evidence of a trade-off within species regarding egg size and egg number is often mixed or absent altogether (e.g., Czesak and Fox 2003 for the seed beetle Stator limbatus, Schwarzkopf et al. 1999 for Drosophila
melanogaster, Allan 1984 for the copepod Mesocyclops, Stearns 1983 for the mosquito fish Gambusia affinis, Reznick 1982 for the guppy Poecilia reticulata).
44 Conclusions and Future Directions The constraint on increased egg diameter (at 6 weeks) in the Pearl Harbor population of Hydroides elegans appears to be selective pressure to maintain the optimum male contribution to lifetime reproduction by delaying the shift to the female sex. Considerable genetic variation for egg size, fecundity, and the time to sex change is present in this population and this is not surprising given that this population likely includes substantial genetic diversity. Pearl Harbor is an extremely busy international port, and H. elegans is a cosmopolitan member of the biofouling community that is commonly found on ship and boat hulls, water intakes, and other underwater structures, the population in Pearl Harbor likely has been assembled from multiple founding populations. One way to test the hypothesis whether the hermaphroditic life style is constraining egg size is to perform a phylogenetic analysis that maps egg size and sex system onto a phylogeny of family Serpulidae and reconstructing ancestral transitions. This type of cladistic analysis was used by Rouse and Fitzhugh (1994) to test whether broadcast spawning and planktonic larvae are pleisiomorphic for the polychaete family Sabellidae. Another set of questions that arise from these results concerns the traits of sperm that are produced by larger-egg selected hermaphrodites. It has been suggested (Levitan 1993, 1998) that sexual selection acts on gamete traits to produce suites of co-adapted traits that include egg size, egg number, sperm velocity, and sperm longevity. Do sperm traits vary with egg traits as selection for increased egg size proceeds? How correlated are sperm traits and egg traits within individuals, within the population? The observed variation in size of males suggests additional work on sex change in this animal. It is reported that all individuals change sex, but many males remaining in
45 the population at 6 weeks were considerably larger than females. Allsop and West (2003) showed that the relative timing of sex change was invariant across broad taxonomic groups and largely predicted by maximum body size, that is, that a sex change should occur at 72% of maximum body size. Data collected in this study do not provide a way to test this prediction but population level studies would be a useful approach to this question. This same data set could also inform us concerning the genetic variation for maximum body size and the trade-off between growth and fecundity at the population level. Reznick et al. (2000) pointed out that studies evaluating life-history traits (and the trade-offs between them) necessarily focus on specific characters. The choice of what components of fitness are included in a study can make the difference between detecting a fitness trade-off or not, since the influence of correlations between unmeasured traits is not known. As efforts to examine the genetic basis of trade-offs broaden to include marine invertebrate life-history evolution, methods that are the most integrative across the life cycle (including various developmental stages/ages/sizes) and across the breadth of traits that define a life history may be the most effective. Large sample sizes are often required to detect genetic correlations using breeding designs and this is reasonable in insect systems. Frequently in marine invertebrate systems this is a logistical impossibility because culture of the larvae is time-, space-, and labor-intensive. It is difficult to detect complex or unexpected patterns in studies that examine correlations across a single generation when sample sizes become limiting. These patterns may be more apparent against a dynamic background where observations are made across multiple life-history stages and generations.
46
4 3.5 3 2.5 2 1.5 1 0.5 0 Gen 6
Gen 7
Gen 8
Gen 9
Gen 10
Gen 11
Generation
Figure 3-1. Cumulative response to selection for increased egg diameter in H. elegans was positive through Generation 11. No error bars were calculated because this is the difference between the mean of 3 selected lines and the mean of 3 control lines at each generation beginning in the base population (Generation 6) and ending at the end of selection (Generation 11). Table 3-1. Egg diameter (µm) in replicate selected vs. control lines of Hydroides elegans after 4 generations of selection; Fully nested ANOVA Source df EMS (X 10-4) F P Treatment 1 147.0604 95.7328 0.0006 Line (Treat) 4 01.5686 6.1680 0.0001 Cross (Line (Treat)) 428 0.2545 18.1511 0.0001 Error 3916 0.0140 --Table 3-2. Total egg energy in replicate selected vs. control lines of Hydroides elegans (calculated as µg C egg-1); Fully nested ANOVA Source df EMS (X 10-4) F P Treatment 1 2.535578 9.8169 0.0350 Line (Treat) 4 0.258603 2.3369 0.0611 Cross (Line (Treat)) 90 0.111605 1.6279 0.0032 Error 174 0.0686 ---
47 Table 3-3. Absolute fecundity in replicate selected vs. control lines of Hydroides elegans (eggs female-1); Fully nested ANOVA Source df EMS (X 106) F P Treatment 1 443.82396 10.5232 0.0304 Line (Treat) 4 42.662385 1.9105 0.1078 Error 403 22.330157 --Table 3-4. Relative fecundity based on dry weight of the female in replicate selected vs. control lines of Hydroides elegans (eggs mg-1); Fully nested ANOVA Source df EMS (X 106) F P Treatment 1 795.873456 6.0931 0.0679 Line (Treat) 4 132.548182 2.5540 0.0386 Error 403 51.897613 --Table 3-5. Adult female dry weight (mg) in replicate selected vs. control lines of Hydroides elegans; Fully nested ANOVA Source df EMS F P Treatment 1 0.025218 0.2290 0.6567 Line (Treat) 4 0.112206 2.8075 0.0253 Error 432 0.0399669 --Table 3-6. Larval volume (µL) at 18 to 20 h post-fertilization in replicate selected vs. control lines of Hydroides elegans; Fully nested ANOVA Source df EMS (X 10-4) F P Treatment 1 0.650836 1.1703 0.3392 Line (Treat) 4 0.558838 1.5227 0.2048 Cross (Line (Treat)) 69 0.366555 0.9246 0.6495 Error 648 0.3964 --Table 3-7. Volume (µL) of competent (5 d) larvae in replicate selected vs. control lines of Hydroides elegans; Fully nested ANOVA Source df EMS (X 10-6) F P Treatment 1 2.44511 4.9009 0.0894 Line (Treat) 4 0.50505 1.8355 0.1324 Cross (Line (Treat)) 66 0.276535 4.9538 0.0001 Error 641 0.0006 --Table 3-8. Juvenile tube length (mm) at 21 d in replicate selected vs. control lines of Hydroides elegans; Fully nested ANOVA Source df EMS F P Treatment 1 47.0398 3.7050 0.1249 Line (Treat) 4 12.6558 0.6682 0.6162 Cross (Line (Treat)) 69 19.16195 4.7420 0.0001 Error 558 4.0409 ---
48 Table 3-9. Summary of direct and correlated responses to selection for increased egg diameter in replicate selected v controls lines of Hydroides elegans. All significant differences represent positive correlations Trait Selected Mean (± SE) Control Mean (± SE) 49.23 (0.35) 45.46 (0.083) Egg d (µm) Total Energy 0.37 (0.17) 0.29 (0.18) -1 (mJ egg ) 18 to 20 h larval 1.12 X10-4 (0.064 X 10-4) 1.14 X10-4 (0.047 X 10-4) Vol (µL) 5 d larval Vol 1.29 X 10-3 (0.041 X 10-3) 1. 16 X 10-3 (0.036 X 10-3) (µL) 21 d Juvenile tube 8.08 (0.31) 8.60 (0.10) length (mm) Adult female dry 0.80 (0.019) 0.82 (0.026) weight (mg) Fecundity (eggs) 10071 (481) 7936 (418) 13451 (834) 10462 (798) Relative Fecundity (eggs mg-1) * P < 0.05. + P < 0.10. NS P > 0.10
* * NS +
NS NS * +
Table 3-10. Effect of selection (treatment) on the relative numbers of males and females in Generations 7 to 11; Model I ANOVA Source df EMS F P Treatment 1 1.3958 6.28 0.0122 Gen 4 0.3852 1.73 0.1395 Gen*treat 4 0.1717 0.77 0.5427 Error 3461 0.2221 --Table 3-11. Mean percent females present at spawning (6 weeks post-fertilization) in replicate selected vs. control lines of Hydroides elegans in Generations 7 to 11 Mean Percent Females in Mean Percent Females in Selected Lines (SE) Control Lines (SE) Generation 7 64.70 (9.036) 61.86 (2.281) Generation 8 64.88 (2.299) 59.21 (2.291) Generation 9 72.11 (5.564) 61.72 (0.877 Generation 10 70.45 (9.022) 62.61 (6.820 Generation 11 74.30 (8.661) 64.21 (3.071 Grand Mean 69.29 (1.935) 61.92 (0.809
CHAPTER 4 CONCLUSIONS The goal of this study was to investigate the evolvability of the trait of egg size, to examine the direct and correlated responses to selection on increased egg size in a specified set of life-history characters, and to explore how these correlations might change as egg size was increased by artificial selection in the polychaete worm
Hydroides elegans. Life-history traits examined included egg diameter, fecundity, relative fecundity, total egg energy (at 6 weeks), larval size at 18 to 20 h, larval size at competence (5 d), tube length at 21 d, and adult dry weight (at 6 weeks). I have used various analytical techniques to show that there is significant additive genetic variation for egg size in the Pearl Harbor population of H. elegans. The response of 2.5 σP to direct selection on egg size indicates that there is substantial potential for egg size to increase in response to selective pressures (Chapter 2). I predicted that there would be negative correlations between at least some fitness-related traits, because we expect alleles underlying positive genetic correlations to be rapidly fixed in natural populations. Yet, I found that large-egg selected females produced more eggs, with higher energy content, that grew into larger larvae at competence. I have proposed that the constraint on increased egg diameter (at 6 weeks) in the Pearl Harbor population of Hydroides
elegans appears to be selective pressure to maintain the optimum male contribution to lifetime reproduction by delaying the shift to the female sex (Chapter 3). Phenotypic correlations between the trait of egg diameter and the suite of fitness-related traits outlined above were estimated using bivariate analysis on replicate 49
50 line means (n = 3 lines treatment-1) in JMP 5.1 (SAS Institute, Inc.). The results comparing control with selected line means can be seen as Pearson product moment correlations (r) in Table 4-1. Among lines the mean values for controls showed no phenotypic correlation between egg diameter and any of the traits of interest, with the exception of larval size at competence (5 d) where a significant positive correlation (0.98) was found. This relationship persisted in selected line means (0.99). However, despite the analysis at the level of treatment showing positive correlations between egg diameter and fecundity, examination of individual selected lines showed a significant negative correlation between egg diameter and both measures of fecundity (-0.95 and -0.99 respectively). The selected lines also showed a significant positive correlation between egg diameter and female dry weight (0.99). A pattern is suggested in the differences between control and selected lines with respect to these phenotypic correlations; the replicate selected line that achieved the highest mean egg diameter also had the highest female dry weight and the lowest fecundity. This pattern (the largest mothers producing the largest eggs in the fewest numbers) is reminiscent of the predicted trade-off between growth, egg size, and fecundity that I did not detect between treatments (Chapter 3). This relationship emerges at the extreme end of the continuum of reproductive investment (large-egg selected lines) and is not detectable among the control lines. While this observation cannot be considered quantitative (n = 3 is the minimum sample size for a correlation), it suggests that further study into the influence of trade-offs in defining reproductive investment might be most fruitful at the extreme ends of the investment continuum in this species.
51 Within polychaetes, fecundity within species can vary with nutritional state of the mother, population density, and adult age and size (Eckelbarger 1986). In this experiment all animals were fed ad libidum at all stages of development, while density and adult age were controlled. Varying any of these parameters or inducing environmental stress at different developmental stages might also reveal evidence of trade-offs influencing reproductive effort. Qiu and Qian (1998) looked at effects of varying salinity and temperature on juvenile traits in H. elegans, and found that fecundity was affected by the stress of low salinity. Czesak and Fox (2003) found while working with the seed beetle Stator limbatus that the magnitude of the tradeoff between egg size and fecundity varied between environments. Another possible cost associated with increased reproductive effort is higher mortality, as was found in the polychaete Dinophiilus gyrociliatus by Prevedelli and coworkers (Prevedelli and Zunarelli Vandini 1999, Prevedelli and Simonini 2000). They found that higher food led to increased fecundity but was accompanied by greater and earlier mortality. Tatar et al. (1993) nicely demonstrated the tradeoff between increased egg production and increased age-specific mortality in the beetle Callosobruchus
maculatus. Many avenues of inquiry can be pursued based on this study. A large body of work has been compiled investigating the adaptive significance of developmental mode in marine invertebrates using comparative, empirical, and manipulative techniques. A great deal of effort has also been invested in quantitative modeling approaches that have been used to try and identify selection pressures and processes that influence developmental mode evolution. The suite of characteristics that defines a developmental type has
52 co-evolved in concert and compromise with a wider complex of life-history traits under the influence of natural selection. The most rewarding efforts to pursue these dynamic and sometimes subtle relationships will be methods that are the most integrative across the stages that define a life cycle, and across the breadth of traits that define a life history. Understanding the nature of the variation in fitness-related traits and how it is partitioned in a particular population has the potential to reveal the insights we seek concerning the evolution of the diverse life histories among marine invertebrates. Table 4-1. Phenotypic correlations between the trait of egg size and a suite of life-history traits in replicate selected and control lines in the polychaete Hydroides elegans, based on line means (n = 3 lines treatment-1). Pearson product moment correlations (r) with absolute value > 0.95 indicated with * Correlation coefficient (r) among Correlation coefficient (r) among Control Line Means (n = 3) Selected Line Means (n = 3) Egg d Fecundity 0.09 Egg d Fecundity -0.95* Relative Relative -0.99* Egg d 0.24 Egg d Fecundity Fecundity Female Dry Female Dry Egg d -0.05 Egg d 0.99* Weight Weight Total energy Total energy Egg d -0.48 Egg d -0.28 -1 egg egg-1 Larval size Larval size Egg d -0.13 Egg d -0.63 at 18 to 20 h at 18 to 20 h Larval size Larval size Egg d 0.98* Egg d 0.99* at 5 d at 5 d Tube length Tube length Egg d -0.86 Egg d -0.91 at 21 d at 21 d
LIST OF REFERENCES Allan, J.D. 1984. Life history variation in a freshwater copepod: evidence from population crosses. Evolution 38:280-291. Allsop, D.J., and S.A. West. 2003. Changing sex at the same relative body size. Nature 425:783-784. Arcos, F.G., I.S. Racotta, and A.M. Ibarra. 2004. Genetic parameter estimates for reproductive traits and egg composition in Pacific white shrimp Penaeus (Litopenaeus) vannamei. Aquaculture 236:151-165. Azevedo, R.B.R., V. French, and L. Partridge. 1996. Thermal evolution of egg size in Drosophila melanogaster. Evolution 50:2338-2345. Azevedo, R.B.R., V. French, and L. Partridge. 1997. Life-history consequences of egg size in Drosophila melanogaster. American Naturalist. 150:250-282. Bakker, K. 1969. Selection for rate of growth and its influence on competitive ability of larvae of Drosophila melanogaster. Netherlands Journal of Zoology. 19:541-595. Barnes, H., and M. Barnes. 1965. Egg size, nauplius size, and their variation with local, geographical and specific factors in some common cirripedes. Journal of Animal Ecology 34:391-402. Bell, A.E., C.H. Moore, and D.C. Warren. 1955. The evaluation of new methods for the improvement of quantitative characteristics. Cold Spring Harbor Symposia on Quantitative Biology. 20:197-212. Berglund, A. 1990. Sequential hermaphroditism and the size-advantage hypothesis: an experimental test. Animal Behavior 39:426-433. Bernardo, J. 1996. The particular maternal effect of propagule size, especially egg size: patterns, models, quality of evidence and interpretations American Zoologist 36:216-236. Blanckenhorn, W.U., and A. Heyland. 2004. The quantitative genetics of two life history trade-offs in the yellow dung fly in abundant and limited food environments Evolutionary Ecology 18:385-402. Bouchet, P. 1989. A review of poecilogony in gastropods. Journal of Molluscan Studies 55:67-78.
53
54 Bradshaw, W.E., and C.M. Holzapfel. 1996. Genetic constraints to life-history evolution in the pitcher-plant mosquito, Wyeomyia smithii. Evolution 50:1176-1181. Brakefield, P.M. 2003. Artificial selection and the development of ecologically relevant phenotypes. Ecology 84:1661-1671. Bridges, T.S., and S. Heppell. 1996. Fitness consequences of maternal effects in Streblospio benedicti (Annelida: Polychaeta). American Zoologist 36:132-146. Carpizio-Ituarte, E., and M.G. Hadfield. 1998. Stimulation of metamorphosis in the polychaete Hydroides elegans Haswell (Serpulidae). Biological Bulletin 194:14-24. Caswell, H. 1981. The evolution of “mixed” life histories in marine invertebrates and elsewhere. American Naturalist 117:529-536. Charnov, E.L. 1979a. Natural selection and sex change in pandalid shrimp: a test of a life history theory. The American Naturalist 113:715-734. Charnov, E.L. 1979b. The genetical evolution of patterns of sexuality: Darwinian fitness. The American Naturalist 113:465-480. Charnov, E.L. 1982. The theory of sex allocation. Princeton University Press. Princeton, NJ. 355 p. Cheverud, J.M. 1984. Quantitative genetics and developmental constraints on evolution by selection. Journal of Theoretical Biology 110:155-171. Chia, F.-S. 1974. Classification and adaptive significance of developmental patterns in marine invertebrates. Thalassia Jugoslavica 10:121-130. Christiansen, F.B., and T.M. Fenchel. 1979. Evolution of marine invertebrate reproductive patterns. Theoretical Population Biology 16:267-282. Clarke, A. 1993. Egg size and egg composition in polar shrimps (Caridea; Decapoda) Journal of Experimental Marine Biology and Ecology 168:189-203. Collin, R. 1995. Sex, size, and position: a test of models predicting size at sex change in the protandrous gastropod Crepidula fornicata. The American Naturalist 146:815831. Collin, R. 2001. Mode of development, phylogeography, and population structure of North Atlantic Crepidula (Gastropoda: Calyptraeidae) species. Molecular Ecology 10:2249-2262. Cunningham, C.W. 1999. Some limitation of ancestral character-state reconstruction when testing evolutionary hypotheses. Systematic Biology 48:665-674.
55 Czesak, M.E., and C.W. Fox. 2003. Evolutionary ecology of egg size and number in a seed beetle: genetic trade-off differs between environments. Evolution 57:11211132. Duda, T.F., and S.R. Palumbi. 1997. Developmental shifts and species selection in gastropods. Proceedings of the National Academy of Science USA 96:1027210277. Ebert, D. 1993. The trade-off between offspring size and number in Daphnia magna: the influence of genetic, environmental and maternal effects. Archiv für Hydrobiologie Supplement 90:453-473. Eckelbarger, K.J. 1986. Vitellogenic mechanisms and the allocation of energy to offspring in polychaetes. Bulletin of Marine Science 39:426-443. Edmands, S., and J.S. Harrison. 2003. Molecular and quantitative trait variation within and among populations of the intertidal copepod Tigriopus californicus. Evolution 57:2277-2285. Emlet, R.B. 1995. Developmental mode and species geographic range in regular sea urchins (Echinodermata: Echinoidea). Evolution 49:476-489. Emlet, R.B., and O. Hoegh-Guldberg. 1997. Effects of egg size on postlarval performance: experimental evidence from a sea urchin. Evolution 51:141-152. Emlet, R.B., L.R. McEdward, and R.R. Strathmann. 1987. Echinoderm larval ecology viewed from the egg. pp. 55-136. In: Jangoux, M. and J.M. Lawrence (eds.) 1987. Echinoderm studies. Balkema. Rotterdam. Englert, D.C., and A.E. Bell. 1969. Components of growth in genetically diverse populations of Tribolium castaneum. Canadian Journal of Genetics and Cytology 11:896-907. Englert, D.C., and A.E. Bell. 1970. Selection for time of pupation in Tribolium castaneum. Genetics 64:541-552. Ernande, B., P. Boudry, J. Clobert, and J. Haure. 2004. Plasticity in resource allocation based life history traits in the Pacific oyster, Crassostrea gigas. I. Spatial variation in food abundance. Journal of Evolutionary Biology 17:342-356. Ernande, B., J. Clobert, H. McCombie, and P. Boudry. 2003. Genetic polymorphism and trade-offs in the early life-history strategy of the Pacific oyster, Crassostrea gigas (Thunberg, 1795): a quantitative genetic study. Journal of Evolutionary Biology 16:399-414. Falconer, D.S., and T.F.C. Mackay. 1996. Introduction to quantitative genetics. Prentice Hall. London. 464 p.
56 Fischer, K., B.J. Zwaan, and P.M. Brakefield. 2004. Genetic and environmental sources of egg size variation in the butterfly Bicyclus anynana. Heredity. 92:163-169. Fox, C.W. 1993. Maternal and genetic influences on egg size and larval performance in a seed beetle (Callosobruchus maculatus): multigenerational transmission of a maternal effect? Heredity. 73:509-517. Fox, C.W., and M.W. Czesak. 2000. Evolutionary ecology of progeny size in arthropods. Annual Review of Entomology 45:341-369. George, S.B. 1999. Egg quality, larval growth and phenotypic plasticity in a forcipulate seastar. Journal of Experimental Marine Biology and Ecology 237:203-224. Ghiselin, M.T. 1969. The evolution of hermaphroditism among animals. Quarterly Review of Biology 44:189-208. Gibson, G.D. 1993. Developmental variability and the induction of metamorphosis in Haminaea callidegenita (Mollusca: Opisthobranchia). Zoology. Edmonton, Alberta, University of Alberta: 134 p. Giménez, L. 2002. Effects of prehatching salinity and initial larval biomass on survival and duration of development in the zoea 1 of the estuarine crab, Chasmagnathus granulata. Journal of Experimental Marine Biology and Ecology 270:93-110. Giménez, L., and K. Anger. 2003. Larval performance in an estuarine crab, Chasmagnathus granulata, is a consequence of both larval and embryonic experience. Marine Ecology Progress Series 249:251-264. Giménez, L., K. Anger, and G. Torres. 2004. Linking life history traits in successive phases of a complex life cycle: effects of larval biomass on early juvenile development in an estuarine crab, Chasmagnathus granulata. Oikos 104:570-580. Gosselin, L.A., and P.-Y. Qian. 1999. Analysing energy content: a new micro-assay and an assessment of the applicability of acid dichromate assays. Hydrobiologia 390:141-151. Grant, A. 1983. On the evolution of brood protection in marine benthic invertebrates. American Naturalist 122:549-555. Guillard, R.R.L. 1975. Culture of phytoplankton for feeding marine invertebrates. pp. 2960. In: Smith, W.L. and M.H. Chaney (eds.). Culture of Marine Invertebrate Animals. 1975. Plenum Publishing, New York. Gustafsson, L. 1986. Lifetime reproductive success and heritability: empirical support for Fisher's fundamental theorem. American Naturalist 128:761-764. Hadfield, M.G., and S.E. Miller. 1987. On developmental patterns of opisthobranchs. American Malacological Bulletin 5:197-214.
57 Hadfield, M.G., and M.F. Strathmann. 1996. Variability, flexibility, and plasticity in life histories of marine invertebrates. Oceanologica Acta 19:323-334. Hadfield, M.G., C.C. Unabia, C.M. Smith, and T.M. Michael. 1994. Settlement preferences of the ubiquitous fouler Hydroides elegans. pp. 65-74. In: Thompson, M, R. Nagabhushanam, R. Sarojini, and M. Fingerman (eds.). Recent Developments in Biofouling Control. 1994. Oxford and IBH Publishing Co. Pvt. Ltd. New Delhi. Harshman, L.G., and A.A. Hoffmann. 2000. Laboratory selection experiments using Drosophila: what do they really tell us? Trends in Ecology and Evolution 15:32-36. Hart, M.W. 1995. What are the costs of small egg size for a marine inverterate with feeding planktonic larvae? American Naturalist 146:415-426. Hart, M.W. 1996. Evolutionary loss of larval feeding: development, form and function in a facultatively feeding larva, Brisaster latifrons. Evolution 50:174-187. Harvey, G.T. 1983. Environmental and genetic effects on mean egg weight in Spruce Budworm (Lepidoptera: Tortricidae) Canadian Entomologist 115:1109-1117. Havenhand, J.N. 1993. Egg to juvenile period, generation time, and the evolution of larval type in marine invertebrates. Marine Ecology Progress Series 97:247-260. Havenhand, J.N. 1995. Evolutionary ecology of larval types. pp. 79-122. In: McEdward, L.R. (ed). 1995. Ecology of marine invertebrate larvae. CRC Press. Boca Raton. Hedgecock, D. 1982. Is gene flow from pelagic larval dispersal important in the adaptation and evolution of marine invertebrates? Bulletin of Marine Science 39:550-564. Hendry, A.P., T. Day, and A.B. Cooper. 2001. Optimal size and number of propagules: allowance for discrete stages and effects of maternal size on reproductive output and offspring fitness. American Naturalist 157:387-407. Hilbish, T.J., E.P. Winn, and P.D. Rawson. 1993. Genetic variation and covariation during larval and juvenile growth in Mercenaria mercenaria. Marine Biology 115:97-104. Hill, W.G. 1971. Design and efficiency of selection experiments for estimating genetic parameters. Biometrics 27:293-311. Hill, W.G. 1972. Estimation of realised heritabilities from selection experiments. II. Selection in one direction. Biometrics 28:767-780. Hoagland, K.E., and R. Robertson. 1988. An assessment of poecilogony in marine invertebrates: phenomenon or fantasy? Biological Bulletin 174:109-125.
58 Hohls T. 1998. Reliability of confidence interval estimators under various nested design parental sample sizes. Biometrical Journal 40:85-98. Hoskin, M.G. 1997. Effects of contrasting modes of larval development on the genetic structure of 3 species of prosobranch gastropods. Marine Biology 127:647-656. Houle, D. 1992. Comparing evolvability and variability of quantitative traits. Genetics 130:195-204. Jablonski, D. 1986. Larval ecology and macroevolution in marine invertebrates. Bulletin of Marine Science 39:565-587. Jablonski, D. 1987. Heritability at the species level: analysis of geographic ranges of Cretaceous mollusks. Science 238:360-363. Jaeckle, W.B. 1995. Variation in the size, energy content and biochemical composition of invertebrate eggs: correlates to the mode of larval development. pp. 49-77. In: McEdward, L.R. (ed). 1995. Ecology of marine invertebrate larvae. CRC Press. Boca Raton, FL. Jägersten, G. 1972. Evolution of the metazoan life cycle: a comprehensive theory. Academic Press. London. 282 p. Jarrett, J.N., and J.A. Pechenik. 1997. Temporal variation in cyprid quality and juvenile growth capacity for an intertidal barnacle. Ecology 78:1262-1265. Jones, H.L., C.D. Todd, and W.J. Lambert. 1996. Intraspecific variation in embryonic and larval traits of the dorid nudibranch mollusc Adalaria proxima (Alder and Hancock) around the northern coasts of the British Isles. Journal of Experimental Marine Biology and Ecology 202:29-47. Knapp S.J. 1986. Confidence intervals for heritability for two-factor mating design single environment linear models. Theoretical Applied Genetics 72:587-591. Kohn, A.J., and F.E. Perron. 1994. Life history and biogeography: patterns in Conus. Oxford University Press. New York. 122 p. Koots, K.R., and J.P. Gibson. 1996. Realized sampling variances of estimates of genetic parameters and the difference between genetic and phenotypic correlations. Genetics 143:1409-1416. Kupriyanova, E.K., E. Nishi, H.A. ten Hove, and A.V. Rzhavsky. 2001. Life-history patterns in serpulimorph polychaetes. Annual Review of Oceanography and Marine Biology 39:1-102. Laughlin, R.B., and W. French. 1989. Interactions between temperature and salinity during brooding on subsequent zoeal development of the mud crab Rhithropanopeus harrisii Marine Biology 102:377-386.
59 Leigh, E.G., E.L. Charnov, and R.R. Warner. 1976. Sex ratio, sex change, and natural selection. Proceedings of the National Academy of Science, USA 73:3656-3660. Leonardos, N., and I.A.N. Lucas. 2000. The nutritional value of algae grown under different culture conditions for Mytilus edulis L. larvae. Aquaculture 182:301-315. Lessios, H.A. 1987. Temporal and spatial variation in egg size of 13 Panamanian echinoids. Journal of Experimental Marine Biology and Ecology 114:217-239. Levin, L.A., H. Caswell, K.D. DePatra, and E.L. Creed. 1987. Demographic consequences of larval development mode: planktotrophy vs. lecithotrophy in Streblospio benedicti. Ecology 68:1877-1886. Levin, L.A., and E.L. Creed. 1986. Effect of temperature and food availability on reproductive responses of Streblospio bendicti (Polychaeta: Spionidae) with planktotrophic or lecithotrophic development. Marine Biology 92:103-113. Levin, L.A., and D.V. Huggett. 1990. Implications of alternative developmental modes for the seasonal dynamics and demography of an estuarine polychaete. Ecology 71:2191-2208. Levin, L.A., J. Zhu, and E.L. Creed. 1991. The genetic basis of life-history characters in a polychaete exhibiting planktotrophy and lecithotrophy. Evolution 45:380-397. Levitan, D.L. 1993. The importance of sperm limitation to the evolution of egg size in marine invertebrates. The American Naturalist 141:517-536. Levitan, D.L. 1996. Predicting optimal and unique egg sizes in free-spawning marine invertebrates. The American Naturalist 148:174-188. Levitan, D.L. 1998. Sperm limitation, sperm competition and sexual selection in external fertilizers. pp. 173-215. In: Birkhead, T.R., and A.P. Moller (eds.). Sperm competition and sexual selection.1998. Academic Press. New York. Levitan, D.R. 2000. Optimal egg size in marine invertebrates: theory and phylogenetic analysis of the critical relationship between egg size and development time in echinoids. American Naturalist 156:175-192. Lips, K.R. 2001. Reproductive trade-offs and bet-hedging in Hyla calypsa, a neotropical treefrog. Oecologia 128:509-518. Luttikhuizen, P. C., P.J.C. Honkoop, J. Drent, and J. van der Meer. 2004. A general solution for optimal egg size during external fertilization, extended scope for intermediate optimal egg size and the introduction of don Ottavio 'tango'. Journal of Theoretical Biology 231:333-343. Lynch, M. 1984. The limits to life history evolution in Daphnia. Evolution 38:465-482.
60 Lynch, M., and B. Walsh. 1998. Genetics and Analysis of Quantitative Traits. Sinauer Associates, Inc. Sunderland, MA. 979 p. Maldonado, M., and C.M. Young. 1999. Effects of the duration of larval life on postlarval stages of the demosponge Sigmadocia caerulea. Journal of Experimental Marine Biology and Ecology 232:9-21. Markow T.A., G.A. Clarke. 1997. Meta-analysis of the heritability of developmental stability: a giant step backward. Journal of Evolutionary Biology 10:31-37. Marshall, D.J., C.N. Cook, and R.B. Emlet. 2006. Offspring size effects mediate competitive interactions in a colonial marine invertebrate. Ecology 87:214-225. Marshall, D.J., C.A. Styan, and M.J. Keough. 2002. Sperm environment affects offspring quality in broadcast spawning marine invertebrates. Ecology Letters 5:173-176. McEdward, L.R. 1997. Reproductive strategies of marine benthic invertebrates revisited: facultative feeding by planktotrophic larvae. American Naturalist 150:48-72. McEdward, L.R., and S.F. Carson. 1987. Variation in egg organic content and its relationship with egg size in the starfish Solaster stimpsoni. Marine Ecology Progress Series 37:159-168. McEdward, L.R., and L.K. Coulter. 1987. Egg volume and energetic content are not correlated among sibling offspring of starfish: implications for life-history theory. Evolution 41:914-917. McEdward, L.R., and B.G. Miner. 2001. Larval and life cycle patterns in echinoderms. Canadian Journal of Zoology 79:1125-1170. McMillian, W.O., R.A. Raff, and S.R. Palumbi. 1992. Population genetic consequences of developmental evolution in sea urchins (genus Heliocidaris). Evolution 46:12991312. Miner, B.G., L.A. McEdward, and L.R. McEdward. 2005. The relationship between egg size and the duration of the facultative period in marine invertebrate larvae. Journal of Experimental Marine Biology and Ecology. 321:135-144. Moran, N.A. 1994. Adaptation and constraint in the complex life cycles of animals Annual Review of Ecology and Systematics 25:573-600. Moran, A.L., and R.B. Emlet. 2001. Offspring size and performance in variable environments: field studies on a marine snail. Ecology 82:1597-1612. Moran, N.A. 1994. Adaptation and constraint in the complex life cycles of animals Annual Review of Ecology and Systematics 25:573-600.
61 Mousseau, T.A., and C.W. Fox. 1998. Maternal effects as adaptations. Oxford University Press. New York. 375 p. Mousseau, T.A., D.A. Roff. 1987. Natural selection and the heritability of fitness components. Heredity 59:181-197. Nunney, L. 1996. The response to selection for fast larval development in Drosophila melanogaster and its effect on adult weight: an example of a fitness trade-off. Evolution 50:1193-1204. Palmer, J.O., and H. Dingle. 1986. Direct and correlated responses to selection among life-history traits in milkweed bugs (Oncopeltus fasciatus). Evolution 40:767-777. Parsons, P. 1964. Egg lengths in Drosophila melanogaster and correlated responses to selection. Genetica 35:175-181. Parsons, T.R., Y. Maita, and C.M. Lalli. 1984. A manual of chemical and biological methods for seawater analysis. Pergamon Press. Oxford. 173 p. Partridge, L., and K. Fowler. 1992. Direct and correlated responses to selection on age at reproduction in Drosophila melanogaster. Evolution 46:76-91. Pechenik, J.A. 1999. On the advantages and disadvantages of larval stages in benthic marine invertebrate life cycles. Marine Ecology-Progress Series 177:269-297. Pechenik, J.A., and T.R. Cerulli. 1991. Influence of delayed metamorphosis on survival, growth, and reproduction of the marine polychaete Capitella-sp.-I. Journal of Experimental Marine Biology and Ecology 151:17-27. Pechenik, J.A., T.J. Hilbish, L.S. Eyster, and D. Marshall. 1996. Relationship between larval and juvenile growth rates in two marine gastropods, Crepidula plana and C. fornicata. Marine Biology 125:119-127. Pechenik, J.A., and M.E. Rice. 2001. Influence of delayed metamorphosis on postsettlement survival and growth in the sipunculan Apionsoma misakianum. Invertebrate Biology 120:50-57. Pechenik, J.A., D. Rittschof, and A.R. Schmidt. 1993. Influence of delayed metamorphosis on survival and growth of juvenile barnacles Balanus amphitrite. Marine Biology 115:287-294. Pechenik, J.A., D.E. Wendt, and J.N. Jarrett. 1998. Metamorphosis is not a new beginning. Bioscience 48:901-910. Pernet, B., and W.B. Jaeckle. 2004. Size and organic content of eggs of marine annelids, and the underestimation of egg energy content by dichromate oxidation. Biological Bulletin 207:67-71.
62 Perron, F.E., and R.H. Carrier. 1981. Egg size distributions among closely related marine invertebrate species: are they bimodel or unimodel? American Naturalist 118:749755. Phillips, N.E. 2002. Effects of nutrition-mediated larval condition on juvenile performance in a marine mussel. Ecology 83:2562-2574. Pinheiro, J., and D. Bates. 2000. Mixed-effects models in S and S-plus. Springer-Verlag. New York. 528 p. Podolsky, R.D., and R.R. Strathmann. 1996. Evolution of egg size in free-spawners: consequences of the fertilization-fecundity trade-off. American Naturalist 148:160173. Prevedelli, D., and R. Simonini. 2000. Effecs of salinity and two food regimes on survival, fecundity and sex ratio in two groups of Dinophilus gyrociliatus (Polychaeta: Dinophilidae). Marine Biology 137:23-29. Prevedelli, D., and R. Zunarelli Vandini. 1999. Survival, fecundity and sex ratio of Dinophilus gyrociliatus (Polychaeta: Dinophilidae) under different dietary conditions. Marine Biology 133:231-236. Qian, P.-Y., and J.A. Pechenik. 1998. Effects of larval starvation and delayed metamorphosis on juvenile survival and growth of the tube-dwelling polychaete Hydroides elegans. Journal of Experimental Marine Biology and Ecology 227:169185. Qian, P.-Y., and F.-S. Chia. 1991. Fecundity and egg size are mediated by food quality in the polychaete worm Capitella sp. Journal of Experimental Marine Biology and Ecology 148:11-25. Qiu, J.-W., and P.-Y. Qian. 1997. Combined effects of salinity, temperature and food on early development of the polychaete Hydroides elegans. Marine Ecology Progress Series 152:79-88. Qiu, J-W., and P.-Y. Qian. 1998. Combined effects of salinity and temperature on juvenile survival, growth and maturation in the polychaete Hydroides elegans. Marine Ecology Progress Series 168:127-134. Raff, R. 1987. Constraint, flexibility, and phylogenetic history in the evolution of direct development in sea urchins. Developmental Biology 119:6-19. Ramirez Llodra, E. 2002. Fecundity and life-history strategies in marine invertebrates. pp. 87-170. In: Southward, A.J., P.A. Tyler, C.M. Young, and L.A. Fuiman (eds.). 2002. Advances in Marine Biology. Academic Press. Amsterdam. Ranzoli, F. 1962. Il falso gonocorismo nel ciclo biologico del polichete Hydroides norvegica (Gunn.). Archivio Zoologico 47:1-19.
63 Reznick, D. 1982. The impact of predation on life history evolution in Trinidadian guppies: genetic basis of observed life history traits. Evolution 36:1236-1250. Reznick, D. 1985. Costs of reproduction: an evaluation of the empirical evidence. Oikos 44:257-267. Reznick, D., L. Nunney, and A. Tessier. 2000. Big houses, big cars, superfleas and the costs of reproduction. Trends in Ecology and Evolution 15:421-425. Roff, D.A. 1990. Understanding the evolution of insect life-cycles: the role of genetic analysis. pp. 5-27. In: Gilbert, F. (ed.). Insect life-cycles: genetics, evolution and co-ordination. 1990. Springer Verlag. London. Roff, D.A. 1992. The evolution of life histories: theory and analysis. Chapman and Hall. New York. 535 p. Roff, D.A., and T.A. Mousseau. 1987. Quantitative genetics and fitness: lessons from Drosophila. Heredity 58:103-118. Rose, M.R., J.L. Graves, and E.W. Hutchinson. 1990. The use of selection to probe patterns of pleiotropy in fitness characters. pp. 29-42. In: Gilbert, F. (ed.). Insect life-cycles: genetics, evolution and co-ordination. 1990. Springer Verlag. London. Roughgarden, J. 1989. The evolution of marine life cycles. pp. 270-330. In: Feldman, M.W. (ed.). 1989. Mathematical evolutionary theory. Princeton University Press. Princeton. Rouse, G., and K. Fitzhugh. 1994. Broadcasting fables: is external fertilization really primitive? Sex, size, and larvae in sabellid polychaetes. Zoologica Scripta 23:271312. Rouse, G.W. 2000. Bias? What bias? The evolution of downstream larval-feeding in animals. Zoologica Scripta 29:213-236. Scheltema, R.S. 1989. Planktonic and non-planktonic development among prosobranch gastropods and its relationships to the geographic ranges of species. pp. 183-188. In: Ryland, J.S., and P.A. Tyler (eds.). Reproduction, genetics, and distributions of marine organisms. Olsen and Olsen. Fredensborg, Denmark. Schwarzkopf, L., M.W. Blows, and M.J. Caley. 1999. Life-history consequences of divergent selection on egg size in Drosophila melanogaster. American Naturalist. 29:333-340. Seslija, D., and N. Tucic. 2003. Selection for developmental time in bean weevil (Acanthoscelides obtectus): correlated responses for other life history traits and genetic architecture of line differentiation. Entomologia Experimentalis et Applicata 106:19-35.
64 Sewell, M.A. 1994. Small size, brooding, and protandry in the apodid sea cucumber Leptosynapta clarki. Biological Bulletin 187:112-123. Shaw, R.G. 1987. Maximum-likelihood approaches applied to quantitative genetics of natural populations. Evolution 41:812-826. Sinervo, B. 1990. The evolution of maternal investment in lizards: an experimental and comparative analysis of egg size and its effects on offspring performance. Evolution 44:279-294. Sinervo, B., and L.R. McEdward. 1988. Developmental consequences of an evolutionary change in egg size: an experimental test. Evolution 42:885-899. Smith, C.C., and S.D. Fretwell. 1974. The optimal balance between egg size and number of offspring. American Naturalist 108:499-506. Stearns, S.C. 1983. The genetic basis of differences in life-history traits among six populations of mosquitofish (Gambusia affinis) that shared ancestors in 1905. Evolution 37:618-627. Stearns, S.C. 1992. The evolution of life histories. Oxford University Press. Oxford. Strathmann, R.R. 1978. The evolution and loss of feeding larval stages of marine invertebrates. Evolution 32:894-906. Strathmann, R.R. 1985. Feeding and non-feeding larval development and life-history evolution in marine invertebrates. Annual Review of Ecology and Systematics 16:339-361. Strathmann, R.R. 2000. Functional design in the evolution of embryos and larvae. Cell and Developmental Biology 11:395-402. Tantawy, A.O., and M.R. El-Helw. 1966. Studies on natural populations of Drosophila. V. Correlated response to selection in Drosophila melanogaster. Genetics 53:97110. Tatar, M., J.R. Carey, and J.W. Vaupel. 1993. Long-term cost of reproduction with and without accelerated senescence in Callosobruchus maculatus: analysis of agespecific mortality. Evolution 47:1302-1312. Thorson, G. 1950. Reproductive and larval ecology of marine bottom invertebrates. Biological Reviews of the Cambridge Philosophical Society 25:1-45. Timofeev, S.F., V.V. Sklyar, and M.V. Savinov. 2004. Stabilizing selection on egg size in the euphausiid, Thysanoessa raschii (M. Sars, 1864) (Euphausiacea) in the Barents Sea. Crustaceana 77:265-275.
65 Todd, C.D., and R.W. Doyle. 1981. Reproductive strategies of marine invertebrates: a settlement timing hypothesis. Marine Ecology Progress Series 4:75-83. Tucic, N., I. Gliksman, D. Seslija, O. Stojkovic, and D. Milanovic. 1998. Laboratory evolution of life-history traits in the bean weevil (Acanthoscelides obtectus): the effects of selection on developmental time in populations with different previous history. Evolution 52:1713-1725. Turner, R.L., and J.M. Lawrence. 1979. Volume and composition of echinoderm eggs: implications for the use of egg size in life-history models. pp.25-40. In: Stancyk, S.E. (ed.). 1979. Reproductive ecology of marine invertebrates. University of South Carolina Press. Columbia, SC. Unabia, C.R.C., and M.G. Hadfield. 1999. Role of bacteria in larval settlement and metamorphosis of the polychaete Hydroides elegans. Marine Biology 133:55-64. Vance, R.R. 1973a. On reproductive strategies in marine benthic invertebrates. American Naturalist 107:339-352. Vance, R.R. 1973b. More on reproductive strategies in marine benthic invertebrates. American Naturalist 107:353-361. VanderWerf, E. 1992. Lack's clutch size hypothesis: an examination of the evidence using meta-analysis. Ecology 73:1699-1705. Warren, D.C. 1924. Inheritance of egg size in Drosophila melanogaster. Genetics 9:4169. Warner, R.R. 1984a. Deferred reproduction as a response to sexual selection in a coral reef fish: a test of the life historical consequences. Evolution 38:148-162. Warner, R.R. 1984b. Mating behavior and hermaphroditism in coral reef fishes. American Scientist 72:128-136. Wendt, D.E. 1996. Effect of larval swimming duration on success of metamorphosis and size of the ancestrular lophophore in Bugula neritina (Bryozoa). Biological Bulletin 191:224-233. Wendt, D.E. 1998. Effect of larval swimming duration on growth and reproduction of Bugula neritina (Bryozoa) under field conditions. Biological Bulletin 195:126-135. Wray, G.A. 1996. Parallel evolution of nonfeeding larvae in echinoids. Sysstematic Biology 45:308-322. Wray, G.A., and R.A. Raff. 1991. The evolution of developmental strategy in marine invertebrates. Trends in Ecology and Evolution 6:45-50.
66 Wright, W.G. 1989. Intraspecific density mediates sex-change in the Patellacean limpet Lottia gigantea. Marine Biology 100:353-364. Zwaan, B., R. Bijlsma, and R.R. Hoekstra. 1995. Artificial selection for developmental time in Drosophila melanogaster in relation to the evolution of aging: direct and correlated responses. Evolution 49:635-648.
BIOGRAPHICAL SKETCH I was born in North Carolina and raised in south Florida. I have traveled extensively as an adult, and settled in Texas where I renewed my pursuit of education and received an Associate of Arts degree from Texas Southmost College in Brownsville, Texas and a Bachelor of Science degree, summa cum laude, from Texas A&M University. I earned my Master of Science degree from Florida Institute of Technology in 2000 and continued to earn my Ph.D. in 2006 from the University of Florida with a major in zoology.
67