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    Reproductive effort in ninespine stickleback (Pungitius pungitius): evidence of terminal

    investment.

    J. Gary Palmer

    Department of Biology

    Northern Michigan University

    1401 Presque Isle Ave.

    Marquette, MI 49855

    [email protected]

    Word count: 2270

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    Animals that mate more than once in their lifetimes (iteroparity) should optimize reproductive

    effort for maximum lifetime reproductive success. Each bout of reproduction comes at the potential

    expense of production of future offspring. This is known as the reproductive cost of mating. The other

    component of reproductive effort is energetic cost, or the amount of energetic resources an individual

    allocates to reproduction. Three separate hypotheses have been proposed as rules governing the

    distribution of reproductive effort. This study sought to test which of these best explains the pattern of

    reproductive effort in the life history of male ninespine stickleback. In an attempt to control costs of

    reproduction among fish of varying ages, individuals were reared in isolation and fed a standardized

    amount of food based on their body weight. Mass of sperm produced in individuals either one or three

    years old was measured and standardized for body weight. This was used as an indicator of energetic

    allocation to reproduction. It was found that on average three-year-old males produced nearly twice as

    much sperm relative to their body weight as did one-year-old individuals. Two-year-old males

    produced an intermediate amount of sperm. Three-year-old males also scored highest in a measure of

    sperm motility and spent the most time fanning eggs in their nest. Results supported the terminal

    investment hypothesis, while finding no evidence supporting senescence or the mating strategy-effort

    hypothesis.

    Keywords: Life history theory, ninespine stickleback, parental investment,Pungitius pungitius,

    reproductive effort, senescence, terminal investment.

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    There is substantial cost borne by parents when producing offspring. Consequently, heavy

    investment in a parent's current brood may come at the expense of future reproduction (Trivers 1972).

    This is considered the reproductive cost of breeding. Another factor in cost of breeding which is

    suspected to be related with this is the energetic cost of breeding, or the amount of energy a parent

    invests in a brood (Clutton-Brock 1984). Energetic cost is much more commonly studied, since it can

    be measured more directly and over a shorter time period through quantifying the energy allocated to

    production of gametes or measuring weight loss over the breeding season. The reproductive cost is

    much more difficult to measure. It requires determining impact on a individual's future survival and any

    change caused in future brood sizes, both of which would require considerable effort to make a record

    of and be difficult to interpret.

    Three hypotheses have been proposed to explain optimal allocation of reproductive effort over

    an iteroparous animal's life history. First and perhaps most well known of these is the terminal

    investment hypothesis. This trade-off between production of current and future offspring should favor

    greater investment in current reproduction as parents age and chance of future reproduction decreases

    (Clutton-Brock 1984). As an individual ages the proportion of it's lifetime remaining diminishes, and

    consequently future reproductive possibilities decline. The result of this is a lowered reproductive cost

    of breeding for older individuals since there are few future broods which could be negatively impacted

    by current breeding efforts.

    An alternative hypothesis is known as the senescence hypothesis. This states that as an animal

    ages, reproductive effort will decrease due to loss of function associated with aging. leading to

    decreased performance. This hypothesis refers specifically to the absolute amount of reproductive

    effort an individual expends, whereas the terminal investment hypothesis specifies that the costs of

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    reproduction must be taken into account. A decrease in ability could cause a decline in absolute output

    even though output relative to ability may increase. It is likely that older individuals incur higher costs

    of breeding, either due to poorer body condition entering the reproductive season (Mysterud et al.

    2001) or decreased ability to defend a territory. These costs must be accounted for or held constant in

    order to accurately determine whether a terminal decline in reproductive output is due to increased

    costs or decreased investment. Because of this difference, the senescence and terminal investment

    hypothesis are not mutually exclusive (Weladji et al. 2002).

    A third hypothesis, proposed by Yoccoz et al. (2001), is the mating strategy-effort hypothesis.

    This predicts a peak in reproductive effort in individuals just beyond maturity. This is based on the idea

    that intrasexual competition plays a large role in reproductive success of males in many species, and

    that investment should be highest when there is the greatest chance of success. In red deer it was found

    that male reproductive effort increased quickly between maturity and peak age then slowly declined

    (Yoccoz et al. 2001). Male reproductive success varies greatly based on number of mates (Trivers

    1972) and investment during peak years should lead to greater benefit in this respect than toward the

    end of the lifespan, when chance of success in these contests is low (Graves, in press).

    One problem encountered in past tests of these hypotheses is that parental investment is

    specifically defined as effort relative to costs, and costs may differ among individuals. For example, in

    species with indeterminate growth such as many fishes, older individuals will be larger than young

    ones and may be able to make a much larger absolute investment in reproduction without necessarily

    investing more relative to the costs. This is further complicated by the tendency for larger individuals to

    be dominant, giving them greater access to resources.

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    This study attempts to control for these factors by raising individuals from eggs under

    controlled laboratory settings in order to maintain constant resource availability and by measuring

    sperm production relative to the weight of each individual. This should eliminate biases found in

    natural settings that favor older individuals and may exaggerate any evidence of terminal investment. It

    is hypothesized that when energetic costs are held constant, relative investment will be found to

    increase with age.

    METHODS

    To test these hypotheses data on sperm production was collected from male ninespine

    stickleback (Pungitius pungitius), an iteroparous fish which can be easily bred in the laboratory. It has

    been shown in male stickleback that individuals vary resource allocation based on reproductive

    strategy, with production of sperm being a useful indicator of allocation (de Fraipoint et al. 1993). The

    individuals used in this experiment were descended from a population of ninespine stickleback

    captured in Lake Superior near Marquette, Michigan. A total of 50 individuals (25 male, 25 female)

    were captured during September 2003 and placed in a large aquarium to establish a large freely

    breeding population. A proportion of haphazardly selected offspring were reared in isolation, and

    month and year of birth was recorded for each individual. This was done to control for differences in

    energetic costs and availability of resources to an individual based on competitive interactions which

    may change over the course of an individuals life in addition to facilitating separation of individuals

    into age classes. These individuals were weighed bimonthly after reaching maturity and given food

    daily in proportion to their weight. This was done to ensure all individuals had equal energetic

    resources, controlled for differences in body mass. Individual fish were raised in 5 gallon aquaria

    maintained at 20 C with a 12:12 light:dark cycle.

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    Subjects for the experiment were chosen haphazardly from the available stock of healthy

    individuals. Subjects were taken from three distinct age classes; one year old plus or minus 2 months

    (n=20), two years old plus or minus 2 months (n=20), and three years old plus or minus 2 months

    (n=20). To assess body condition a standard curve was created using data from all available males

    raised in isolation (n=79). Body length was plotted against mass and a least squares linear regression

    line was drawn. Individuals whose mass differed from the expected according to this curve by more

    than 20% were not included in this experiment.

    To measure sperm production the collection procedure from de Fraipoint et al. (1993) was used.

    Each male was placed upside-down in a slit cut into a wet sponge and pressure was gently applied to

    the abdomen. This resulted in secretion of milt and glue, which were easily distinguished and

    separated. Sperm was collected from each individual three times, each time separated by 48 hours. The

    masses recorded from these three collections were averaged for each individual then divided by body

    mass and multiplied by 100 in order to obtain a standardized index of sperm production relative to

    body mass. There was no apparent change in mass of sperm over the three collections for each

    individual.

    In addition to quantity, sperm quality was also assessed. Milt from the second sample taken

    from each male was observed and assigned an ordinal motility score using a procedure similar to that

    found in de Fraipoint et al. (1993). Each male's second sample was used in order to control for any

    differences in motility that may occur as a function of time since last ejaculation. Briefly, sperm were

    collected using a capillary tube then diluted in 5ml distilled water. One drop of this solution was then

    placed on a slide and observed under a microscope. Because the value recorded reflects a proportion of

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    sperm which are motile, it was not crucial to carefully control the volumes placed on the microscope

    slides. Sperm motility values were assigned as follows: 0 if no motility is observed, 1 if most

    spermatozoa are immotile, 2 if most spermatozoa are vibrating, 3 if all spermatozoa are vibrating, 4 if

    most spermatozoa were motile with flagellar movements, and 5 if all spermatozoa were motile with

    flagellar movements (Guest et al. 1976).

    The third portion of the experiment involved observation of egg fanning behavior displayed by

    males. After sperm quantity and motility had been obsesses each of the males included in the study was

    allowed to mate. Males were given 10g (wet weight) ofSpyrogyra algae with which to construct a nest.

    Mates were gravid females, all two years old plus or minus four months. Females were introduced into

    the aquarium of each male 48 hours after the third sperm sample was obtained and allowed to remain

    until eggs were deposited, usually occurring within 90 minutes. For the next seven days a group of

    student volunteers observed each male for a 15 minute period between 1400 and 1600 hours each day.

    Time spent fanning eggs was carefully observed and recorded as a proportion of the entire 15 minute

    observation period.

    RESULTS

    All data analysis was performed using SPSS 16.0 for Windows. The data collected show a

    significant correlation between length and body mass of a fish (figure 1) (Pearson correlation r= 0.996,

    P< 0.001). This relationship was used to judge the body conditions of individuals used in the study,

    with those falling below the regression line considered in poor condition, and those above in good

    condition. Age was also found to be significantly correlated with body mass (Pearson correlation r=

    0.985,P< 0.001). Body mass also correlated significantly with mass of sperm produced (Pearson

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    correlation r= 0.954,P< 0.001). This supports the assumption that older males will be larger and

    produce more sperm, therefore cost of sperm production must be standardized by body size.

    Sperm mass index data for individuals of all three age classes were assumed to be normally

    distributed according to a Shapiro-Wilk test (one year: T20 = 0.925,P=0.124; two year: T20=0.952,

    P=0.406, three year: T20 = 0.948, P= 0.340). Data for sperm mass were also assumed to have equal

    variance (Levene's Test for Homogeneity of VarianceF= 0.673,P= 0.514). Using one-way ANOVA a

    significant difference was found in in the mean sperm production index among the age classes (F2,59 =

    196.029, p < 0.001). A Tukey's HSD post-hoc test showed that sperm mass was significantly higher for

    second-year than first-year males (P

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    among the age classes (F2,59=198.834,P

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    It would be of interest to test these hypotheses through measurement of sperm production in

    other species, particularly ones in which this is the only means of male parental investment.

    Stickleback males provide a great deal more investment than just gametes, they construct and defend a

    nest as well as fanning eggs during brooding. It is possible due to the relatively low cost of sperm

    production that this is only a minor component of a male stickleback's parental investment and different

    effects would be seen if other measures of parental investment were used.

    References

    Clutton-Brock, T. H. 1984. Reproductive effort and terminal investment in iteroparous animals.

    American Naturalist, 123, 212-229.

    De Fraipont, M., Fitzgerald, G. J., & Guderly, H. 1993. Age-related differences in reproductive

    tactics in three-spined stickleback, Gasterosteus aculeatus. Animal Behaviour, 46, 961-968

    Graves, B. M. 2008.Ritualized Fighting and Life History Evolution in Human Males.In press.

    Mysterud, A., Yoccoz, N.G., Stenseth, N.C., & Langvatn, R. 2001. Effects of age, sex, and density

    on body weight of Norweigan red deer: evidence of senescence. Proceedings of the Royal Society

    of London B, 268, 911-919.

    Guest, W.C., Avault, J.W., & Roussel, J.D. 1976. A spermatology study of channel catfish,Ictalurus

    punctatus. Transactions of the American Fisheries Society, 105, 463-468.

    Trivers, R. L. 1972. Parental investment and sexual selection. In: Sexual Selection and the

    Descent of Man 1871-1971. (Ed. by B. Campbell), pp. 136-179. Chicago, Illinois: Aldine.

    Weladji, R. B., Mysterud, A., Holand, ., & Lenvik, D. 2002. Age-related reproductive effort in

    reindeer (Rangifer tarandus): evidence of senescence. Oecologia, 131, 79-82

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    Yoccoz, N. G., Mysterud, A., Langvatn, R., & Stenseth, N. C. 2002. Age- and density-dependent

    reproductive effort in male red deer.Proceedings of the Royal Society of London B, 269, 1523-

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    Figure 1: Length vs. body mass of male stickleback. Males of three different ages were measured and

    weighed to construct a standard curve in order to assess body condition. Data from all individuals

    available (n=79) are included.

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    Figure 2: Average sperm production by age. The sperm production index, calculated for each individual

    by dividing mass of sperm by body mass, was averaged for each age group. The data show that on

    average this index was twice as high for three-year-old individuals as one-year-olds.

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    Age vs. average sperm production index

    Age of individuals (years)

    Averagesperm

    productionin

    dexvalue

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    Figure 3: Average sperm motility score by age. Sperm motility was ranked on a scale of 0-5, with 0

    representing no motility observed and 5 representing all spermatozoa motile with flagellar movement

    (Guest et al. 1976).

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    0.5

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    Age vs. average sperm motility score

    Age of individuals (years)

    Averagesperm

    motilityscor e

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    Figure 4: Average proportion of time fanning eggs. The proportion of time during a 15 minute

    observation window that a male spent fanning eggs was recorded daily for seven days immediately

    following fertilization of eggs by the male.

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    0.5

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    Age vs. proportion of time spent fanning

    Age of individuals (years)

    Proportionoft i

    mespentfan

    ningeggs

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