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AMER. ZOOL., 23:25-34 (1983) Alternative Concepts of Reproductive Effort, Costs of Reproduction, and Selection in Life-History Evolution1 JUHA TUOMI Department of Biology, University of Turku, SF-20500 Turku 50, Finland TUOMO HAKALA Department of Biomedicine, University of Turku, SF-20500 Turku 50, Finland AND ERKKI H A U K I O J A Department of Biology, University of Turku, SF-20500 Turku 50, Finland SYNOPSIS. An outline for an organismic theory of reproductive tactics is presented to develop the demographic theory of optimal reproductive tactics into a more realistic theory of life-history evolution. Reproductive effort—denned as the proportion of resources invested in reproduction—and the costs in somatic investment do not automatically result in survival costs. Both the conditions where survival costs are produced and the conditions where reproduction can take place without survival costs are specified. Compensation and threshold hypotheses are put forward to allow weaker correlations between reproduction and survival than the trade-off hypothesis, which assumes direct impacts by reproductive effort on survival. Furthermore, reproductive tactics are unlikely to be moulded by the demographic forces of selection only. An empirical example is shown where residual reproductive value played no significant role in the evolution of reproductive tactics. Selection probably operates not on separate life-history traits but on whole organisms through their entire life-history. The structural and physiological intercouplings between separate traits can result in phenotypic opportunity sets where selection can mould lifehistory traits only within the constraints of the opportunity sets. Optimization theory has provided an efficient technique for modelling and making predictions. However, organismic selection does not necessarily optimize adaptive strategies but eliminates unfit strategies. Life-history theory, and evolutionary theory in general, can be developed along alternative logical lines when different hypotheses are generated on how selection operates. INTRODUCTION optimized by maximizing fitness under the The demographic theory of optimal re- P u r e l y demographic forces of selection, productive tactics, first postulated by WilAlthough demographic theory is logiliams (1966a, b), is based on three basic c a l l y s o u n d > a n d several predictions have ideas—reproductive effort, costs of repro- b e e n derived for empirical tests, its asduction, and selection as a process of de- sumptions may be violated on several critmographic optimization. Demographic >cal points, where alternative logical paths theory has been formulated by assuming diverge. Assumptions other than those that reproductive effort entails a fixed conventionally made can lead to different trade-off between current and future re- predictions. Therefore, demographic theproductive success, and that reproductive ory represents only a specific line of reaeffort, and life-history traits in general, are soning and a specific approach to life-history evolution. This paper outlines several alternatives in relation to reproductive effort, costs of 1 From the Symposium on The inter-face of Life-His- reproduction, and selection. Restrictions tory Evolution, whole-Organism Ontogeny and Quantita- ', , r • u • , tive Genetics presented at the Annual Meeting of the a n d w e a k P a r t s o f demographic theory are American Society of Zoologists, 27-30 December also pointed out. T h e possibilities not COn1981, at Dallas, Texas. ventionally taken into account are sum25 26 TUOMI ET AL. • '• B1 i I • B3 FIG. 1. The same absolute investments in reproducB2systems where tion (Ir) produced by four allocation somatic investments of reproductive individuals (I,) vary in relation to the standard level of somatic investments of nonreproductive individuals (In). The resources for reproduction can be produced at the expense of somatic investments (A) or by increasing resource input (Bl and B2) or by both means (B3). marized as a preliminary outline for an organismic theory of reproductive tactics. REPRODUCTIVE EFFORT Reproductive effort (E) was introduced as a measure of both the fraction of resources invested in reproduction and the costs of reproduction in somatic investments. This definition implied a direct trade-off: an increase in reproductive effort increases current reproductive output at the expense of survival due to reduced somatic investment (Williams, 1966a, b; Gadgil and Bossert, 1970). This definition of reproductive effort can be used properly only when resources are invested in reproduction at the same rate that reproduction drains resources from somatic investment. This concept loses accuracy if resources are invested in reproduction at a different rate than they are drained from somatic investment. Resources could be invested in reproduction only partially at the expense of somatic investment, and perhaps at no expense to somatic investment in certain cases. Several definitions and indices of reproductive effort have been suggested (Hirshfield and Tinkle, 1975; Leon, 1976; Randolph et al., 1977; Haukioja and Hakala, 1978; Calow, 1979). The problem is that demographic theory is based on a definition logically different from that of most empirical studies. Furthermore, the conventional definition (E) of reproductive effort is an adequate measure only in one allocation system. Allocation systems Reproductive effort is always defined in relative terms, but the definitions can be treated best after the parameters dictating resource partitioning have been defined in absolute terms.The somatic investment of nonreproductive individuals (In) can be taken as the standard against which other investments are compared. The total investment (Ia) of reproductive individuals consists of somatic investment (Is) and reproductive investment (Ir) I. = I. + IrThe absolute costs to somatic investment caused by reproduction are given by RS = In - I, and the absolute amount of resources produced by differences in resource input between reproductive and nonreproductive individuals is given by Ra = la - InThe inconsistencies between definitions of reproductive effort are due to the fact that the same absolute investment in reproduction can be produced by different systems of allocation (Fig. 1). (We ignore the costs of resource processing.): A. B. Both reproductive and nonreproductive individuals have equal resources available for investment (Ia = In). Then all resources invested in reproduction are produced at the cost of somatic investment, and Ir = Rs and Ra = 0. The total amount of resources avail- 27 ALTERNATIVE CONCEPTS IN LIFE-HISTORY EVOLUTION able for the investment of reproductive individuals exceeds the level of nonreproductive individuals (Ia > In). Bl. All resources produced by the increased resource input are invested in reproduction and there are no costs to somatic investment (Is = In). Then Ir = Ra and Rs = 0. B2. There are no costs to somatic investment and only part of the resources produced by the increased resource input is invested in reproduction (Is > In). Then Ra > Ir > 0 and Rs < 0. B3. All resources produced by the increased resource input are invested in reproduction and there are costs to somatic investment (Is < In). Then Ir = Rs + Ra where Rs > 0 and Ra > 0. Here Ir, Rs, and Ra are the basic parameters of reproduction which describe various aspects of resource investment in absolute terms. A satisfactory theory of reproduction must be able to treat all such systems of allocation, in both absolute and relative terms. For this purpose, either a definition of reproductive effort must be found which is accurate in all allocation systems, or the concept of reproductive effort must be defined separately for each allocation system. Definitions and their limitations The meaning of the term "reproductive effort" varies depending on the components of resource investment included in the definition. Here we consider some definitions which are based on the absolute basic parameters mentioned above: RE = I r /I. RES = (In - In = R s /I n and REa = (I. - I n )/I, = R./I,. Given specific allocation systems, other alternatives exist: E = I r /I. = R s /I n and RE, = I r /I, = R./I,. The first specific definition (E) refers to allocation system A. Here RE = RES and E TABLE 1. Alternative definitions of reproductive effort (E, /?£„ and RE) and allocation systems (Fig. I). * Allocation systems A E; RE = RE, RE,; RE = RE, RE RE, RE, Bl B2 B3 + + + + + 0 + 0 + + + * The relative costs in somatic investment (RE,) and the proportion of resources produced by the increased resource input (REa) are also shown. The values of RE, can vary from positive to negative depending on the allocation systems. + + equals both the proportion of resources invested in reproduction and the costs to somatic investment. This definition can be used only if Ia = In and Ir = Rs. RE and RES can be denoted by E in allocation system A but not in Bl, B2, and B3. The second specific definition (RE,) is reproductive effort defined for allocation system B1 where RE = REa, Is = In, and Ir = Ra. Here RE, equals both the fraction of resources invested in reproduction and the proportion that increased resource input forms of the total investment of reproductive individuals. Although there is no need to define RE and REa separately in allocation system Bl, they must be kept separate in both B2 and B3. Consequently, E and RE; are very limited definitions of reproductive effort for allocation systems A and Bl respectively (Table 1). RE is the best candidate for the general definition of reproductive effort, because it can be used in all allocation systems (Table 1). However, RE indicates only the fraction of resources invested in reproduction. It does not necessarily imply any trade-off between reproduction and somatic investment. If RE is taken as the standard definition of reproductive effort, theories of reproductive tactics could operate in all allocation systems, but then reproductive effort is a purely descriptive concept which does not specify the sources of the resources invested in reproduction. The resources can be produced at the cost of somatic resources a n d / o r by increasing resource input during reproduction. RES (the stress of reproduction; somatic 28 TUOMI ET AL. costs) measures the costs to somatic investment. It indicates the proportion of resources invested in reproduction only in allocation system A. Allocation system B2 is a special case where RES is negative and reproductive individuals invest more resources in somatic investment than do nonreproductive individuals. REa (resource increment) indicates the proportion of increased resource input from the total investment of reproductive individuals. It does not generally measure the proportion of resources invested in reproduction, excluding allocation system B1, or the costs to somatic investment. The distinction among RE, RES, and REa suggests a revision of our view of resource allocation. Demographic theory has operated with the special definition (E) of reproductive effort limited to allocation system A. Since this special definition cannot be used in all allocation systems, the original concept should be replaced by RE. However, reproductive effort as given by RE is not necessarily a biologically useful quantity because offspring production may not be restricted by the values of RE as such, but by the causal mechanisms producing resources for reproduction. In such cases, offspring production depends on both (a) the resources invested in reproduction at the cost of somatic investment and (b) the resources which can be made available for reproduction by increasing resource input. Therefore, RES and REa may be biologically more important quantities than reproductive effort (RE). COSTS OF REPRODUCTION The demographic theory of optimal reproductive tactics is based on the idea of a trade-off as implied by allocation system A. This hypothesis (Williams, 19666) can be summarized as three postulates: (1) When both reproductive and nonreproductive individuals have the same limited amount of resources available for investment, an increase in reproductive effort inevitably results in both an increase in current reproductive output and a reduction in somatic investment ("somatic costs"). (2) When reproduction takes place at the expense of somatic investment, the somatic costs reduce the probability of surviving to the next breeding season ("survival costs") and/or reduce future reproductive output ("fecundity costs"). (3) When reproduction results in survival and/or fecundity costs, there is a tradeoff between current reproductive output and residual reproductive value. However, the postulates of the trade-off hypothesis do not necessarily hold in allocation systems other than A. First, increased resource input can uncouple somatic costs from the direct influences of reproductive effort. Reproduction can take place only partially or not at all at the expense of somatic investment. Second, reproductive individuals can adapt to resist somatic costs, within specific limits, without any survival costs. Thus reproduction need not automatically result in survival costs, although survival and fecundity costs can be indirect results of reproduction in critical environmental conditions. (Fecundity costs are neglected below.) Somatic costs: compensation hypothesis The stress of reproduction defined as RES = (In - I5)/In = (In - I. + I r )/I n measures the somatic costs of reproduction by the extent to which reproduction reduces the somatic investment of reproductive individuals below the standard level of nonreproductive ones living in the same environmental conditions. As with the trade-off hypothesis, reproductive effort (RE) equals RES when resource availability is the same for the investment of both reproductive and nonreproductive individuals. Then In = L,, RES = I r /I a = RE, and RE always results in corresponding somatic costs as indicated by RES. But the situation is fundamentally different when reproductive individuals can increase their Ia above the level of nonreproductive individuals (In). The increased resource input (or some part of it) can be invested in either reproduction or compensation for the somatic costs caused by ALTERNATIVE CONCEPTS IN LIFE-HISTORY EVOLUTION I UJ o < o / R * \ /.._JL_\.__ ; \ i i 1 / \ > R» / 4/ CO 1 29 REPRODUCTION i Fie. 2. The absolute investments in reproduction (Ir) produced by the increment (Ra) in resource input and by the reduction (R,) in somatic resources. The weight of nonreproductive individuals (Wn) is assumed to remain constant while the somatic weight of reproductive individuals (Wr) fluctuates in time due to reproduction. reproduction. In both cases, increased resource input results in a reduction of RE5 because now RES = I r /I n - (I, - I n )/I n = (I a /I n )RE - R a /I n which is the equation of a straight line with slope I a /I n and the intercept - R a / I n (see Fig. 3, below). Since the resources increase, the somatic investment of reproductive individuals is reduced below the level of nonreproductive individuals only when RE > (I, - I n )/I a = REa. When reproductive effort (RE) is equal to REa, reproduction is not associated with somatic costs because RES = 0. When RE is smaller than REa, reproductive individuals allocate more resources to soma than nonreproductive individuals. Therefore, RES can be negative if reproductive effort is low enough. (For an example, see the Anodonta population n:o 550 in Fig. 5.) There are at least two ways in which reproductive individuals can increase their Ia above the level of In. First, they can in- FIG. 3. The maximum reproductive effort without survival costs in the trade-off hypothesis (RE,), the compensation hypothesis (RE2), and the threshold hypothesis (RE/ and RE2') when the line RE, = C/I n represents the threshold value of somatic costs (RE,). crease their resource intake and ingestion during reproductive period above the level of nonreproductive individuals (Randolph etal., 1977). Second, reproductive individuals could invest more resources in somatic growth prior to reproduction and transfer this increment in somatic resources later to offspring production (Fig. 2). In the latter case, the extra resources accumulated during somatic growth form the resource pool for reproduction, and reproduction would result in seasonal fluctuations in the weight of reproductive individuals, as reported in fish (lies, 1974). The weight of nonreproductive individuals can also fluctuate, but the amplitude of fluctuations should be higher in reproductive individuals if this mechanism is operating. Survival costs: threshold hypothesis If somatic costs are assumed to result in survival costs, then maximal reproductive effort without any somatic costs and survival costs is RE, = 0, when Ia = In. The corresponding maximal effort is RE2 = REa > 0, when reproductive individuals are able to increase their Ia above the level of In (Fig. 3). Then reproduction can take place without somatic and survival costs only if RE < REa. A further possibility is that somatic costs do not entail equivalent survival costs. 30 TUOMI ET AL. This is not an unrealistic possibility because resource shortage does not automatically mean a shorter life-span. On the contrary, moderately starved animals can live even longer than animals feeding ad libitum {e.g., Ross and Bras, 1975). This shows that a decrease in somatic investments does not necessarily lead to survival costs, and indicates that organisms may have physiological mechanisms which allow them to resist moderate resource deficiencies. However, it is not clear how closely this situation resembles the resource deficiency caused by the somatic costs of reproduction. In some plants, reproduction per se seems to be the cue leading to the death of the parent individual (Woolhouse, 1978). But, among iteroparous organisms, there are probably cases where parents suffer survival costs due to the somatic costs of reproduction only when the somatic investments are reduced below a specific minimum level, say ln — C. Then survival costs would occur only when Is < In — C and reproductive effort is maximal without survival costs when Is = In — C and RES = C/I n . Physiological resistance to somatic costs could allow the maximum effort to increase above RE, and RE2 without survival costs. When Ia = In, this maximum level of effort would be RE,' = C/I a = C/I n , where RE,' > 0 if C > 0. When Ra > 0 and C > 0, the maximum effort without survival costs would be RE2' = (C + R a )/I a , where RE2' > RE2 > 0 (Fig. 3). Here C/I n is the threshold value of RES. Reproduction produces no survival costs when somatic costs remain below the threshold level. But the survival of reproductive individuals would decrease when somatic costs exceed the threshold level. The threshold hypothesis might explain some physiological aspects of age-specific variation in reproductive effort (RE) and somatic costs (RES) in species where individual organisms invest resources in reproduction only to the extent that such investment does not reduce their own survival. Resistance to somatic costs (Svardson, 1949), as well as the ability to compensate for somatic costs by means of increased resource input, can vary with the age and/or size of individuals. The threshold value of RES could also depend on the environment (Haukioja and Hakala, 1979) and the physiological state of the individuals themselves. Direct and indirect survival costs Reproduction can result in survival costs, or it may entail no somatic costs and/or no survival costs. A reduced level of somatic investment could lead to survival costs in two ways. First, somatic costs can result in direct survival costs when the reduced level of somatic investment as such reduces the survival of reproductive individuals. When reproductive effort approaches 1.0 (Fig. 3), somatic costs could become so high that the reduced level of somatic investment itself leads to the death of reproductive individuals. However, reproduction may not lead to direct survival costs with low or moderate reproductive effort. Second, reproduction could also produce indirect survival costs when somatic costs cause no direct survival costs but increase the vulnerability of reproductive individuals to predators (Shine, 1980), disease (Hirshfield, 1980), or other critical factors in the environment (Haukioja and Hakala, 1979). Indirect survival costs arise only when a specific critical factor of the environment is present. Consequently, several causal paths could result in survival costs, but it is conceivable that nearly as many do not. Therefore, theories of reproductive tactics require alternative models, with and without survival costs. Theory and experiment should address three questions: (1) Does reproduction generally lead to survival costs? (2) What are the causal mechanisms producing survival costs when they arise? (3) Are survival costs generally highenough to produce significant effects on the evolution of reproductive tactics? Demographic optimality models have simply assumed ineluctable mechanisms which ALTERNATIVE CONCEPTS IN LIFE-HISTORY EVOLUTION REPRODUCTIVE VALUE AI THE AGE X+l A!iD SURVIVAL 1YPOTHETICAL GEHES OF ALLOCATION AT THE AGE ) FECUNDITY COSTS CURRENT REPRODUCTIVE OUTPUT AT THE AGE X RESIDUAL REPRODUCTIVE VALUE AT THE AGE X RRV. REPRODUCTIVE VALUE AT ~THE AGE X SELECTION FOR OPTIMAL TACTiCS DEPENDING ON PAYOFFS IN FITNESS FIG. 4. An outline of the demographic theory of optimal reproductive tactics. Age-specific reproductive tactics are assumed to evolve under the purely demographic forces of selection. lead to survival and fecundity costs which have significant evolutionary consequences on reproductive tactics. 31 effort is heritable. Demographic theory has also minimized the role of organisms themselves in the evolution of reproductive tactics. It represents a specific approach to the evolution of reproductive tactics from the purely demographic angle (Stearns, 1980). Selection is supposed to operate on separate life-history traits rather than on individual organisms (Tuomi el al., 1983). We show an example where residual reproductive value seems to play no role in the evolution of age-specific reproductive tactics. We also discuss the role of organismic selection in the evolution of reproductive tactics. A test of the theory One cannot test empirically whether maximizing fitness and reproductive value are equivalent or whether selection maxiSELECTION mizes rm. These questions are primarily Demographic theory compressed natu- theoretical and beyond the scope of direct ral selection into the demographic equa- empirical tests. However, it is possible to tions representing fitness (e.g., intrinsic rate test whether age-specific reproductive tacof increase, rm) and reproductive value (Fig. tics correlate with RRV. Williams (19666) 4). Williams (\966b) proposed that selec- predicted a negative correlation between tion optimizes reproductive tactics at each reproductive effort and residual reproducage depending on reproductive value mod- tive value. This prediction can be tested by ified by current reproductive output and comparing age-specific values of reproducresidual reproductive value (RRV). Schaf- tive effort and RRV within the same popfer (1974) derived an analytical model by ulation. But the prediction should also hold assuming that maximizing fitness and re- when comparing the same age-classes beproductive value are equivalent. Later, a tween different populations. Also in this number of models were generated to pre- case, there should be a negative correlation dict age-specific variation in reproductive between reproductive effort and RRV, if effort {e.g., Pianka and Parker, 1975; reproductive effort is optimized in each Charlesworth and Leon, 1976; Stearns, population depending on RRV. 1976; Bell, 1980). Mantyla (1981) has studied the age-speHowever, the mathematical basis of de- cific reproductive tactics of a freshwater mographic theory has been questioned. It mussel, Anodonta piscinalis (Unionidae), in is not clear whether maximizing fitness and eight local populations. He estimated reproductive value are always equivalent "reproductive effort" by using the index (Schaffer, 1979, 1981; Caswell, 1980; RE5 = (Wn - W r )/W n Ricklefs, 1981), and maximizing rm, or other abundance measures of fitness, is itself which corresponds to the present definia questionable evolutionary principle tion of somatic costs. The index (Haukioja (Yodzis, 1981). Other fitness definitions are and Hakala, 1978) measures how much the available, too (Stearns, 1983; Stearns and somatic weight of reproductive individuals Crandall, 1981). Furthermore, the biolog- (Wr) is reduced during reproduction below ical basis of demographic theory is highly the somatic weight of individuals of the simplified. No evidence has been presented same age in the nonreproductive stage (Wn). that age-specific variation in reproductive RE5 was observed to increase almost lin- 32 TUOMI ET AL. TABLE 2. Correlations of the index of somatic costs (REJ with current reproductive output mo residual reproductive value RRVa and the ratio mx/RRVx in three age-classes of Anodonta piscinalis." 403020- Age-class (x) 4yr "" 5yr 10- m, RRV X m x /RRV x <n 111 tr <H r AGE 0.845** -0.109 0.891** 0.830* -0.056 0.833* • The correlations were calculated by comparing the eight populations shown in Figure 5. From Mantyla (1981). *P < 0.05, ** P < 0.01. -10- i 0.836** -0.245 0.860** (YEARS) Fic. 5. Age-specific trends in the index of somatic costs (RE,) in eight populations of Anodonta piscinalis (Mollusca, Unionidae) studied by Mantyla (1981). early with age in all the populations studied (Fig. 5). But there was no clearly inverse relation between RES and RRV within the populations because RRV increased in young age-classes, at least up to the 4th year of life. The increase in fecundity more than compensated for adult mortality in RRV, which began to decrease only in the very old age-classes. Furthermore, there was no significant correlation between RES and RRV when the same age-classes were compared between the populations (Table 2). The results indicate that RRV as such played little or no role in the evolution of reproductive tactics in Anodonta piscinalis. The ratio between current reproductive output and residual reproductive value (m x /RRV x ) gave statistically significant correlations, obviously due to the strong correlations between RES and mx (Table 2). It seems that in Anodonta populations reproductive tactics were not moulded by purely demographic forces of selection, at least not by RRV alone. Major factors moulding the reproductive tactics of Anodonta might be physiological processes modified by environmental resource availability and other environmental factors (see also Haukioja and Hakala, 1978). Selection and organisms Life-history models describe selection as a demographic abstraction where each lifehistory trait is separately optimized de- pending on payoffs in fitness. For simplicity, physiology and ontogeny are omitted (Stearns, 1980). However, it is useful to study how the reasoning of demographic theory changes if selection is assumed to operate on whole organisms, rather than on separate life-history traits (Table 3). Separate life-history traits have no independent existence in nature; they are always dependent upon the structural and functional organization of an individual organism. Therefore, individual life-history traits are not free to coevolve under the purely demographic forces of selection. Structural, physiological and developmental constraints can restrict the potential evolutionary trajectories (Stearns, 1977, 1980; Gould and Lewontin, 1979). This suggests the need for a shift from unconstrained to constrained optimization, where the constraints determine the boundaries of opportunity sets—the sets of feasible phenotypes on which selection can operate. In such theory, selection is assumed to mould the life-history strategies of organisms only within species-specific opportunity sets. The structural and physiological organization of an individual organism can also result in intercouplings between individual life-history traits. Then a change in one trait could be automatically associated with changes in other traits (e.g., when either evolutionary or purely phenotypic changes in developmental and growth rates automatically cause changes in the age of maturity and generation time). It is quite possible that the syndromes generalized as the ALTERNATIVE CONCEPTS IN LIFE-HISTORY EVOLUTION r/K-continuum (Pianka, 1970) reflect just these intercouplings and not ecological selection pressures as assumed in the theory of r and K-selection. Naturally the truth could lie somewhere between these two possibilities if both physiological intercouplings and the ecological conditions of living restrict the possible combinations of life-history traits. A further problem goes back to Darwin, who assumed that natural selection operates in the same way as artificial selection, allowing only the fittest to persist in the population. If selection operates as conventional artificial selection, it would be an extremely effective and sensitive evolutionary mechanism, which could modify the adaptive strategies of organisms in every detail. However, an alternative hypothesis for the operation of natural selection has been suggested (e.g., Stearns, 1983; Tuomi et al., 1983). Natural selection operating on whole organisms need not necessarily operate in the same way as artificial selection, but rather as negative mass selection (Wright, 1980), in which deleterious mutants and unfit phenotypes are eliminated, without precise optimization. Demographic theory is based on the implicit assumption that in nature organisms follow only the best possible strategies of reproduction. But in fact nature can be less perfect (Darlington, 1977; Gould and Lewontin, 1979), if organisms follow strategies that are satisfactory or "good enough" in given ecological conditions, but not necessarily "optimal" in any sense (Stearns, 1983). Optimality models have been effective tools for making predictions in life-history evolution, but that selection always operates in nature with the precision of optimization is only a theoretical possibility. DISCUSSION The value of life-history theory as a whole for the biological sciences has been not so much that it has successfully explained variation in life-history traits, but that it has brought the deficiencies of evolutionary theory into critical and open-minded discussions. Evolutionary theory has 33 TABLE 3. A comparison of demographic theory with the present outline for an organismic theory of reproductive tactics. Demographic theory 1. Resource limitation; allocation system A; reproductive effort (E). Trade-off between current reproductive output and survival and/or future fecundity. Separate life-history traits are free to coevolve under purely demographic forces. Selection operates on separate traits. Selection optimizes adaptive strategies. Organismic theory 1. Allocation systems A, Bl, B2, and B3; reproductive effort (RE); somatic costs (RE,); resource increment (RE,). 2. Compensation for somatic costs; cost thresholds; direct and indirect survival costs. 3. Constraints and opportunity sets; physiological intercouplings between traits. 4. Selection operates on whole organisms. 5. Selection eliminates unfit phenotypes but does not necessarily optimize adaptive strategies. undergone fundamental conceptual changes since Darwin (Tuomi, 1981). Darwin formulated the general framework for evolutionary theory, but his outline lacked genetic, ontogenetic, and ecological mechanisms and details. The founders of theoretical population genetics together with their modern followers have enriched the original framework with detailed genetic analyses and quantitative modelling. This development culminated in the synthetic theory, where population genetics was taken as the logical core of evolutionary theory as a whole. However, it has become evident that while population genetics is an essential speciality of evolutionary theory, ontogeny and ecology must also be taken into account in evolutionary theorizing. 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