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Beyond the Fast-Slow Continuum of Life Histories
Iain Stott1 , Rob Salguero-Gómez1 , Owen Jones1 , Thomas Ezard1 , Jean-Michel Gaillard1 ,
Marlène Gamelon1 , Dave Hodgson1 , Shelly Lachish1 , Jean-Dominique Lebreton1 , and
Emily G Simmonds1
1
Affiliation not available
July 25, 2023
Beyond the Fast-Slow Continuum of Life Histories
A manuscript in preparation as an invited Opinion for TREE
Iain Stott1,2,* , Roberto Salguero-Gómez3,* , Owen R Jones2 , Thomas HG Ezard4 , Jean-Michel Gaillard5 ,
Marlène Gamelon5,6,7 , Shelly Lachish3 , Jean-Dominique Lebreton8 , Emily G Simmonds7,9 , and Dave J
Hodgson10
*Shared first authors
1
Department of Life Sciences, University of Lincoln, Lincoln LN6 7TS, UK
2
Department of Biology, University of Southern Denmark, Odense 5230, Denmark
3
Department of Biology, University of Oxford, Oxford, OX1 3SZ, UK
4
School of Ocean and Earth Science, University of Southampton, European Way, Southampton SO14 3ZH,
UK
5
Laboratoire de Biométrie et Biologie Evolutive UMR 5558, CNRS, Université Claude Bernard Lyon 1,
69622, Villeurbanne, France
6
Department of Biology, Norwegian University of Science and Technology, 7491, Trondheim, Norway
7
Centre for Biodiversity Dynamics, Norwegian University of Science and Technology, 7491, Trondheim,
Norway
8
Centre d’Ecologie Fonctionelle & Evolutive, CNRS Montpellier, Montpellier 34293, France
9
Department of Mathematical Sciences, Norwegian University of Science and Technology, 7034, Trondheim,
Norway
10
Department of Ecology & Evolution, University of Exeter, Penryn TR10 9FE, UK.
Keywords
Comparative demography, life history theory, life history strategy, life history trait, reproductive tactic,
phylogenetic comparative analyses
HIGHLIGHTS
1
Posted on 25 Jul 2023 | The copyright holder is the author/funder. All rights reserved. No reuse without permission. | https://doi.org/10.22541/au.169029175.51225048/v1 | This a preprint and has not been peer reviewed. Data may be preliminary.
* Open-access life history data have proliferated dramatically in recent years and macro-ecological studies
are using these data to examine patterns in life histories across the tree of life.
* These studies support the fast-slow continuum being the dominant – but not unique – axis structuring life
history variation: other important axes associated with development, reproductive tactics, and demographic
buffering have emerged.
* Here, we make recommendations for characterising life history through data choices and analytical methods
of dimensionality reduction, with recourse to a clear model of life history.
* We use our framework to advocate that future empirical studies of life history evolution take hypothesisdriven approaches that investigate classical and emerging life history theories, to reveal novel axes, clusters,
and boundaries of life history variation across all taxa.
ABSTRACT
Life history theory is key to understanding Earth’s diverse life forms. Indeed, schedules of survival, development, and reproduction are the filters through which natural selection acts on species’ heritable traits to
shape fitness. Prevailing wisdom places species’ life history strategies along a fast-slow axis of variation.
Challenges to the unicity of this axis are increasingly frequent, given proliferation of life history databases
and availability of sophisticated multivariate statistical techniques. However, these empirical approaches
often lack concrete theoretical or hypothetical foundations. We advocate for using standardised traits, targeting data gaps and overcoming focus on taxonomic siloes, to facilitate a hyopthesis-driven approach in
future examination of drivers of life history variation across the whole Tree of Life.
MAIN TEXT
Any individual is born, survives, develops, possibly reproduces, and ultimately dies. There are countless
pathways through life, and as such there is a tremendous diversity of life history strategies (see Glossary)
across species. However, such strategies are not always associated with species’ evolutionary history or
environment (Box 1). Central aims of evolutionary ecology include describing and explaining the diversity
of life histories across the Tree of Life [1]. In this context, the fast-slow continuum [2] has become the
standard framework. Indeed, the fast-slow continuum describes a high amount of life history variation across
species in most taxonomic groups studied so far [3–9]. However, beyond this fast-slow continuum, many
comparative studies have identified various other important axes of variation, often linked to developmental
or reproductive tactics.
Around the inception of the fast-slow continuum, Stearns [2] suggested that there was not yet a “general and
reliable theory of life history evolution” and that the field was not“empirically sufficient” to test life history
theory. With the emergence of large global databases of demographic and trait data [10–18], we are now
much closer in several taxonomic groups to the required sufficiency to test general theories of life history
evolution. However, the challenges of identifying, quantifying, explaining, and inferring life history diversity
has quickly become lost in a fog of data types, trait currencies, statistical confounds, non-independence,
mathematical artefacts, and eco-evolutionary feedbacks.
So although the fast-slow continuum is the main structuring axis of life history variation across species
studied to date, it is not by itself an adequate universal theory of life history, and there remains little
consensus on how to measure life history [19] and which interspecific patterns deserve explanation. As such,
we still lack a“general and reliable” [2] understanding of life history diversity.
Here, we reflect on the state-of-the-art in life history theory and the potential for general theories in the
context of further axes of life history variation beyond the fast-slow continuum. We identify several empirical
challenges that must be overcome to properly test such theories across the Tree of Life. These challenges
include filling taxonomic and biogeographic data gaps, standardising trait units and developing novel ana-
2
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lytical techniques to facilitate moving toward hypothesis-based over exploratory analyses. Without universal
benchmarks, it will be difficult to determine whether the life history strategies we currently observe in the
wild are shaped by allometry, relatedness, physiologies, bauplan , behaviours, lifestyles, trophic levels, or
biogeographic realms.
LIFE HISTORY THEORY AND THE FAST-SLOW CONTINUUM
The life history of an organism determines its fitness, as life history dictates the numerical representation of
future generations [1]. Life history is therefore the filter via which selection on phenotypic traits operates,
and via which environmental variation generates population,R community, and ecosystem dynamics. This idea
ω
is underpinned by the canonical Euler-Lotka identity 1 = x=1 λ−x lx mx dx, with fundamental components
describing the schedules of survival (lx ) and reproduction (mx ) to the maximum age x =[1]. This identity
characterises how survival and reproduction over the life course (x = age) determines population growth
(λ). However, this equation tells us nothing about potential covariation between survival and reproduction,
between early-life and late-life reproduction, or whether age is the best predictor of fitness; indeed, it has
been recently argued that size is a better predictor in many species [20]. A comprehensive theory of life
history strategies must at the very least describe measurable directions and strengths of these potential
trade-offs, but in reality, life history is much more complicated (Box 2).
Schedules of survival and reproduction can be measured in many ways. Examples include life expectancy
, longevity, age at first reproduction, lifetime reproductive output , measures ofactuarial and reproductive senescence , andgeneration time . Although some of these demographic metrics often do a good
job as proxies for life history continua [21], no single one of these life history traits adequately captures
every characteristic of the demographic schedules lx andmx . Therefore, comparative studies often use several
life history traits and apply methods of dimension reduction to yield emergent, composite measures. The
nonlinearity of these schedules, together with the influence of density dependence and stochasticity [22],
complicate measurement of their covariance. These complications remain even if the conceptual framework
describing life history structures and competing processes of energy allocation is relatively well known (Box
2).
The fast-slow continuum [2] remains the standard framework for understanding life history diversity across
the Tree of Life and is characterised using various life history traits mentioned above. ‘Fast’ creatures
tend to have quick development and early-life allocation of resources to profuse reproduction over survival.
‘Slow’ creatures have protracted development, delayed maturation, and allocate resources to survival over
reproduction. The fast-slow continuum continues to emerge as an important explanator of eco-evolutionary
dynamics across taxa, and more recently in the fields of trophic [23] and disease ecology [24] too.
As well as being a canonic ordination of life history variation, the fast-slow continuum predicts species’
response to global change. Compared to fast-lived species, slow-lived species show higher sensitivity of
population growth to sea temperatures in fishes [25], higher extinction rates in mammals and birds [26], and
more negative responses of mammals to human disturbances [27]. These characteristics render long-living
species less resilient than fast-living species to environmental insults, making the populations of the former
more likely to decline (the so-called “malediction of long-lived species” [28]). However, fast species are
more sensitive to increases in temporal autocorrelation of the environment [29]. Such patterns have wider
implications for future ecosystem function [26] and conservation success [30].
MULTIPLE AXES TO GRIND
The fast-slow continuum is almost consistently supported as the dominant but by no means the sole factor
structuring life history variation, including in mammals [3–5], birds [3], insects [6,7], fish [8] and plants
[9] (although the extent of support is sensitive to the life history traits analysed [31]). Exceptions to the
fast-slow ‘rule’ exist, with species having strategies characterised by both high survival and reproduction,
such as marine turtles or trees [32], being especially common. Many such organisms have vital rates closely
related to size and development, for which age is a poor predictor [20]. These life history strategies are
instead defined using a second reproductive axis of variation: how species allocate to reproduction, rather
3
Posted on 25 Jul 2023 — The copyright holder is the author/funder. All rights reserved. No reuse without permission. — https://doi.org/10.22541/au.169029175.51225048/v1 — This a preprint and has not been peer reviewed. Data may be preliminary.
than their reproductive outputper se . The second most dominant axis of variation thus usually relates to
reproductive and developmental tactics, such as fromaltricial vs. precocial offspring [5]; from high to low
recruitment rates [33], high to low frequency of reproduction [7] or from semelparity toiteroparity [3,9].
In some cases, axes other than reproduction explain substantial life history variation, such as age-specific
distributions of mortality and reproduction [34]. The exact meaning of additional axes is hindered by the
vast heterogeneity of life history traits analysed in this context [31].
Additional axes may be required to explain additional peculiarities in post-maturation distributions of agespecific survival and reproduction, such as species that reverse development using shrinkage orretrogression
, or pause development using seed banks or diapause [9].
LIFE HISTORY DATA SOURCES
Quality data for quantifying life histories takes much effort to collect as life histories cannot be described
simply by observing static phenotypes. Measuring life history traits can be challenging: some infrequent, brief
life history events can be at best rarely observed. Examples include reproduction in semelparous perennial
species, or mortality in long-lived species. Much effort has been devoted to the inference of unobserved or
imperfectly detected life history events in population studies [35]. The demographic context of traits like
generation time and life expectancy means that they must be measured using samples of individuals within
populations or species. Hence, life history trait data vary greatly in their abundance, accessibility, and
quality (Table 1) [12,36], even among charismatic species [12].
The gold standard in demographic data is detailed schedules of age- or stage-specific vital rates . These
rates of survival, development, and reproduction are becoming increasingly available through open databases
of demographic data (e.g., [10,11,16–18,31,37,38]). Despite the diversity of model dimensions and complexity,
life history traits can be derived from these schedules, yielding a set of common traits across species. This
derivation overcomes some of the issues with simple trait data outlined in Table 1. Demographic quantities
such as stationary [39] and transient [40] population dynamics can also be calculated from life history
schedules, as can selection pressures [41]. However, although these databases are accessible, models vary
in quality and data remain taxonomically biased [36]. Moreover, the traits derived from these models are
mathematical functions of the same underlying schedules of survival, development, and reproduction, hence
correlations among them are a combination of the real and the artefactual [42].
CURRENCIES OF LIFE HISTORY TRAITS
We identify four key ways to quantify life history data (Box 2). These ways are often linked to hierarchies
of biological organisation and the researcher’s own perspective. These four life history currenciesdefine how
an organism acquires and allocates resources [43], and the consequences for its vital rates. Evolutionary
ecologists typically see the world through an adaptive lens and might study selection strength by measuring
how schedules of life history traits affect fitness. In contrast, behavioural ecologists perceive evolution of
life history in light of an organism’s use of energy or space in acquiring resources, whereas developmental
biologists focus on energy allocation to ontogenetic cellular and organic processes. From a demographer’s
perspective, life histories consist of events measured in time or frequency, as these events capture or directly
affect survival and/or reproduction over age or stage. However, even within these broad perspectives and
currencies, the units of life history trait measurement often vary. For example, demographic measures can be
confused by mixing rates, durations, ages, frequencies, and times-to-events. Currencies can also be confused
by measuring traits in one currency as proxies for processes in another. Examples include using morphological
or behavioural sexual displays as proxies for allocation of energy to reproduction [44], or body size as an
allometric proxy for survival, reproduction, metabolic rate, and use of space [3,5,45,46]). Past comparative
analyses have often been performed on rather heterogeneous life history trait currencies, including the very
first one published by Stearns 40 years ago. The mixture of currencies confounds the interpretation of the
structuring axes of life history variation across the Tree of Life. As such, we urge to standardise the currency
in future analyses to enable cross-study, cross-taxonomic fair comparisons.
STATISTICAL ANALYSIS OF LIFE HISTORY TRAIT DATA
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We argue that alternatives to popular analytical approaches in life history theory should be considered
more often [47], and judiciously applied. Tractable generalisations of life history variation frequently require
analyses to collapse multivariate trait datasets and associated covariates into a smaller set of latent variables.
Common statistical means of reducing dimensionality have both strengths and drawbacks (Box 3). The most
popular approach in this context is the Principal Components Analysis (PCA). Although PCA is a wellestablished exploratory tool, it should not be used naı̈vely [48].
First, researchers should be aware of their own interpretations and biases when interpreting dimension
reduction analyses. Prior to analysis, careful consideration should be given to the aim of the study: for
example, PCA informs on correlative rather than causative relationships between variables. Interpreting
results of multivariate analyses can be challenging, as composite axes are combinations of underlying traits.
Second, careful consideration should be given to how the chosen data may affect outcomes. Indeed, sets of life
history traits that are derived algebraically from vital rate schedules may be correlated due to mathematical
relationships as much as natural covariation [49]. If a trait set includes measures that are a function of multiple
vital rates (e.g ., generation time), or that are measured in different units (e.g ., energy for metabolic rate and
time for mortality), structuring axes from PCAs (principal components) may be challenging to determine.
Even if the multivariate trait set is carefully chosen, it is likely to be difficult to draw fair comparisons
between studies that use different trait sets and therefore have component axes with different orientations.
Third, the statistical shortcomings of analyses must be carefully considered. In particular, a weakness of
PCA is that, in its simplest form, it does not consider measurement errors (but see [50]). Fourth, PCAs do
not account for non-linearities among life history traits [45]. Finally, and perhaps most importantly, inquiry
should be hypothesis-driven: PCA is designed to inform on how variation in multivariate data is partitioned,
rather than to test associations between specific traits (Box 3).
RECOMMENDATIONS FOR AN HYPOTHESIS-DRIVEN, EMPIRICALLY SUFFICIENT
ERA
Recent increases in available life history trait data unlock our ability to further understand the prevailing
patterns of global variation in life history strategies, their evolutionary and ecological drivers and constraints, and their consequences for the extinction risk, invasiveness, and ecosystem functioning. We expand
on Stearns’ [2] original conditions to identify a number of contemporary challenges concerning life history
data and analyses, as we strive to attain the “empirical sufficiency” required to test modern theories of life
history evolution.
Moving towards universal life history traits, derived from demographic schedules of survival,
reproduction and development.Such data can be implicitly measured in a single currency of rates per
standard unit of time [51]. This unit harmonisation will strengthen the links between life history, demography,
and fitness [1], given their explicit treatment of time in the canonical Euler-Lotka equation. Such rates still
need credible transformation during statistical analysis [52]. We further encourage the development of theories
and methods to drive our understanding of life history evolution using state variables that are not measured
using time but linked to other currencies, with energy being a primary candidate.
Filling gaps in life history trait data across the Tree of Life, especially for microbes, fungi, and
invertebrates . There are challenges inherent to this recommendation, since for many organisms we lack
a good working definition of life cycles and life histories, let alone what constitutes an individual, death,
or reproduction. Variation in lifestyle (e.g., sedentary vs. mobile, diet, habitat), bauplan (e.g. , modular vs.
unitary, degree of mobility, brain development), growth pattern (e.g., determinate vs.indeterminate growth)
and reproductive modes (e.g., sexualvs. asexual) further complicate the comparative landscape. Attempt to
fill data gaps should prioritise measures that will facilitate broad comparisons of life history across taxa. As
information gaps across species fill in, it is worthwhile to consider the need for data on vital rate variation
within species [53]. Moreover, time series vital rate data exist for a relatively small number of species, and
so comprehensive assessments of density-dependent mechanisms driving vital rate variation remain rare.
Embracing life history traits comparative across broad taxa and levels of biological organi-
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sation . Besides some exceptions [54,55], multivariate studies seeking to understand axes of life history
variation across kingdoms of life emerged only recently [29,56,57]. Previous studies that have encompassed
a broad taxonomic range were limited to bivariate analyses [55]. Naturally, continuing taxon-specific lines
of enquiry will play an important role, especially in taxa with rich data quality. However, limiting analysis
only to separate groups of organisms implies a perceived wisdom that gross differences in the morphology,
physiology, and lifestyle of different groups will inevitably create different selection pressures on their life
history strategies. This presumption should be backed up with empirical analyses of whether and how the
dominant axes of life history variation change among taxa. Existing evidence is they do not [29].
Achieving consensus regarding evolutionary ancestry across all species to implement robust
phylogenetic analyses. Recent advances in phylogenetics have yielded trees describing the relationships
among species across ever larger taxonomic groups [58–60]. Despite these advances, the details of ancestral
relationships in many parts of these trees, and particularly in deeper evolutionary time, remain debated and
with multiple gaps to fill. We require better consensus on the best way to deal with phylogenetic covariance.
The classic assumption of Brownian trait evolution is often not supported, with increasing recognition for
the need to incorporate evolution towards trait optima and to identify and account for shifts in trait optima
across taxa [61]. There is a strong potential to find patterning in life history strategies common across all
species, but we should be ready to be surprised by deep-rooted differences in how natural selection has
shaped strategies in particular clades.
Adopting analytical approaches that infer explicit links between life history traits and emergent axes of life history variation. We see a role for the wider use of Factor Analysis [47] to help discover
life history axes as latent factors of observed vital rates. Further development of FA algorithms will be key
to help test hypotheses derived from life history theory, and particularly phylogenetically-controlled confirmatory FA methods. We also urge for the development and application of Canonical Correlation Analysis
to reveal associations between the multivariate life history traits of species and their multivariate suites of
demographic, phenotypic, and ecological features.
CONCLUDING REMARKS: ARE ALL SPECIES FAST OR SLOW?
Hypothesis-driven research, rather than exploratory data analyses, should guide the study of multivariate life
history traits and the eco-evolutionary drivers and limits that shape them. Prevailing evidence shows that the
fast-slow continuum is the major structuring axis of life history variation in several taxa, but also that this
continuum alone does not fully describe life history variation. We advocate for the development of further
theory to test hypotheses regarding which axes, clusters, syndromes, and constraints shape said variation.
Likely candidates include different reproductive or developmental tactics (see Outstanding Questions). As we
make further progress in the era of “empirical sufficiency”, we must also take more mechanistic approaches.
These approaches must be coupled with higher-quality data and robust analytical methods. Ultimately,
we argue that more time spent on theory and hypothesis development will lead to more targeted efforts
to better understand how life history strategies are shaped by the environment, ancestry, and bauplan.
Concurrently, the search for universal syndromes of life history across all currencies of measurement must
continue, encompassing the whole Tree of Life.
ACKNOWLEDGEMENTS
T. Coulson provided constructive feedback on an earlier version of this work. IS received funding from
the EU Horizon 2020 research and innovation programme under Marie Sklodowska-Curie Award (MSCA)
grant agreement WHYAGE 746235. RSG was supported by a NERC Independent Research Fellowship
(NE/M018458/1). MG was supported by the Research Council of Norway through its Centres of Excellence
funding scheme (223257), by the CNRS, and by the “PURE” ANR JCJC program.
REFERENCES
1. Metcalf, C.J.E. and Pavard, S. (2007) Why evolutionary biologists should be demographers. Trends Ecol.
6
Posted on 25 Jul 2023 — The copyright holder is the author/funder. All rights reserved. No reuse without permission. — https://doi.org/10.22541/au.169029175.51225048/v1 — This a preprint and has not been peer reviewed. Data may be preliminary.
Evol. 22, 205–212
2. Stearns, S.C. (1977) The evolution of life history traits: a critique of the theory and a review of the data.
Annu. Rev. Ecol. Syst. 8, 145-171
3. Gaillard, J.-M. et al. (1989) An analysis of demographic tactics in birds and mammals. Oikos 56, 59-76
4. Oli, M.K. and Dobson, F.S. (2003) The relative importance of life-history variables to population growth
rate in mammals: Cole’s prediction revisited. Am. Nat. 161, 422–440
5. Stearns, S.C. (1983) The influence of size and phylogeny on patterns of covariation among life-history
traits in the mammals. Oikos41, 173-187
6. Blackburn, T.M. (1991) Evidence for a ‘fast-slow’ continuum of life-history traits among parasitoid
Hymenoptera. Funct. Ecol. 5, 65-74
7. Bakewell, A.T. et al. (2020) Comparing Life Histories across Taxonomic Groups in Multiple Dimensions:
How Mammal-Like Are Insects?Am. Nat. 195, 70–81
8. Rochet, M.-J. et al. (2000) Comparative analysis of phylogenetic and fishing effects in life history patterns
of teleost fishes. Oikos 91, 255–270
9. Salguero-Gómez, R. et al. (2016) Fast-slow continuum and reproductive strategies structure plant lifehistory variation worldwide. Proc. Natl. Acad. Sci. U. S. A. 113, 230–235
10. Salguero-Gómez, R. et al. (2015) The COMPADRE Plant Matrix Database: an open online repository
for plant demography. J. Ecol. 103, 202–218
11. Salguero-Gómez, R. et al. (2016) COMADRE: a global data base of animal demography. J. Anim. Ecol.
85, 371–384
12. Conde, D.A. et al. (2019) Data gaps and opportunities for comparative and conservation biology. Proc.
Natl. Acad. Sci. U. S. A. 116, 9658–9664
13. Kattge, J. et al. (2020) TRY plant trait database–enhanced coverage and open access. Glob. Chang. Biol.
26, 119–188
14. Enquist, B.J. et al. (2016) Cyberinfrastructure for an integrated botanical information network to investigate the ecological impacts of global climate change on plant biodiversity. PeerJ Preprints 4:e2615v2
15. Hintze, C. et al. (2013) D3: The Dispersal and Diaspore Database – Baseline data and statistics on seed
dispersal.Perspect. Plant Ecol. Evol. Syst. 15, 180–192
16. Myhrvold, N.P. et al. (2015) An amniote life-history database to perform comparative analyses with
birds, mammals, and reptiles.Ecology 96, 3109–3000
17. Jones, K.E. et al. (2009) PanTHERIA: a species-level database of life history, ecology, and geography of
extant and recently extinct mammals. Ecology 90, 2648–2648
18. Levin, S.C. et al. (2022) Rpadrino: An R package to access and use PADRINO , an open access database
of Integral Projection Models.Methods Ecol. Evol. 13, 1923–1929
19. Pistón, N. et al. (2019) Multidimensional ecological analyses demonstrate how interactions between
functional traits shape fitness and life history strategies. J. Ecol. 107, 2317–2328
20. Roper, M. et al. (2021) Senescence: why and where selection gradients might not decline with age. Proc.
Biol. Sci. 288, 20210851
21. Gaillard, J.-M. et al. (2005) Generation time: a reliable metric to measure life-history variation among
mammalian populations.The American naturalist , 166, 119–123
7
Posted on 25 Jul 2023 — The copyright holder is the author/funder. All rights reserved. No reuse without permission. — https://doi.org/10.22541/au.169029175.51225048/v1 — This a preprint and has not been peer reviewed. Data may be preliminary.
22. Tuljapurkar, S. et al. (2009) From stochastic environments to life histories and back. Philos. Trans. R.
Soc. Lond. B Biol. Sci. 364, 1499–1509
23. Kiørboe, T. and Thomas, M.K. (2020) Heterotrophic eukaryotes show a slow-fast continuum, not a
gleaner–exploiter trade-off.Proceedings of the National Academy of Sciences 117, 24893–24899
24. Valenzuela-Sánchez, A. et al. (2021) Why disease ecology needs life-history theory: a host perspective.
Ecol. Lett. 24, 876–890
25. Wang, H.-Y. et al. (2020) Life histories determine divergent population trends for fishes under climate
warming. Nat. Commun.11, 4088
26. Cooke, R.S.C. et al. (2019) Projected losses of global mammal and bird ecological strategies. Nat. Commun. 10, 2279
27. Suraci, J.P. et al. (2021) Disturbance type and species life history predict mammal responses to humans.
Glob. Chang. Biol.27, 3718–3731
28. Lebreton, J.-D. (2006) Dynamical and statistical models of vertebrate population dynamics. C. R. Biol.
329, 804–812
29. Paniw, M. et al. (2018) Interactive life-history traits predict sensitivity of plants and animals to temporal
autocorrelation.Ecol. Lett. 21, 275–286
30. Ducatez, S. and Shine, R. (2019) Life-history traits and the fate of translocated populations. Conserv.
Biol. 33, 853–860
31. Gaillard, J.-M. et al. (2021) Applying comparative methods to different databases: lessons from demographic analyses across mammal species. In Demographic Methods across the Tree of Life , pp. 299–312,
Oxford University Press
32. Wright, J. et al. (2020) Contrasting patterns of density-dependent selection at different life stages can
create more than one fast-slow axis of life-history variation. Ecol. Evol.10, 3068–3078
33. Ruger, N. et al. (2018) Beyond the fast-slow continuum: demographic dimensions structuring a tropical
tree community.Ecol. Lett. 21, 1075–1084
34. Healy, K. et al. (2019) Animal life history is shaped by the pace of life and the distribution of age-specific
mortality and reproduction. Nat. Ecol. Evol. 3, 1217–1224
35. Colchero, F. et al. (2012) BaSTA: an R package for Bayesian estimation of age-specific survival from
incomplete mark-recapture/recovery data with covariates. Methods Ecol. Evol.3, 466–470
36. Romer, G. et al. (2021) Plant demographic knowledge is biased towards short-term studies of temperateregion herbaceous perennials.bioRxiv , 2021.04.25.441327
37. Bernard, C. et al. (2023) MOSAIC - A unified trait database to complement structured population
models. Sci. Data 10, 335
38. Lebreton, J.-D. et al. (2012) Towards a vertebrate demographic data bank. J. Ornithol. 152, 617–624
39. Caswell, H. (2001) Matrix Population Models: Construction, Analysis, and Interpretation. 2nd edn
Sinauer Associates. Inc. , Sunderland, MA
40. Stott, I. et al. (2011) A framework for studying transient dynamics of population projection matrix
models. Ecol. Lett. 14, 959–970
41. Silvertown, J. et al. (1993) Comparative plant demography–relative importance of life-cycle components
to the finite rate of increase in woody and herbaceous perennials. J. Ecol. 81, 465
42. Ellner, S.P. (2018) Generation Time in structured populations.Am. Nat. 192, 105–110
8
Posted on 25 Jul 2023 — The copyright holder is the author/funder. All rights reserved. No reuse without permission. — https://doi.org/10.22541/au.169029175.51225048/v1 — This a preprint and has not been peer reviewed. Data may be preliminary.
43. Descamps, S. et al. (2016) When relative allocation depends on total resource acquisition: implication
for the analysis of trade-offs. J. Evol. Biol. 29, 1860–1866
44. Preston, B.T. et al. (2011) Sexually extravagant males age more rapidly. Ecol. Lett. 14, 1017–1024
45. Pelabon, C. et al. (2014) Evolution of morphological allometry. Ann. N. Y. Acad. Sci. 1320, 58–75
46. Voje, K.L. (2016) Scaling of morphological characters across trait type, sex, and environment: a metaanalysis of static allometries.Am. Nat. 187, 89–98
47. Bielby, J. et al. (2007) The fast-slow continuum in mammalian life history: an empirical reevaluation.
Am. Nat. 169, 748–757
48. Peres-Neto, P.R. et al. (2005) How many principal components? stopping rules for determining the
number of non-trivial axes revisited.Comput. Stat. Data Anal. 49, 974–997
49. Ellner, S.P. and Rees, M. (2006) Integral projection models for species with complex demography. Am.
Nat. 167, 410–428
50. Shi, J. and Song, W. (2016) Sparse principal component analysis with measurement errors. J. Stat.
Plan. Inference 175, 87–99
51. Gaillard, J.-M. et al. (2016) Life Histories, Axes of Variation in. In Encyclopedia of Evolutionary Biology
, pp. 312–323, Elsevier
52. McDonald, J.L. et al. (2017) Divergent demographic strategies of plants in variable environments. Nat.
Ecol. Evol. 1, 0029
53. Van de Walle, J. et al. (2023) Individual life histories: neither slow nor fast, just diverse. Proc. Biol.
Sci. 290, 20230511
54. Fenchel, T. (1974) Intrinsic rate of natural increase: The relationship with body size. Oecologia 14,
317–326
55. Blueweiss, L. et al. (1978) Relationships between body size and some life history parameters. Oecologia
37, 257–272
56. Salguero-Gomez, R. and Jones, O.R. (2017) Life history trade-offs modulate the speed of senescence.
In The Evolution of Senescence in the Tree of Life (Shefferson, R. P. et al., eds), pp. 403–421, Cambridge
University Press
57. Hatton, I.A. et al. (2019) Linking scaling laws across eukaryotes. Proc. Natl. Acad. Sci. U. S. A. 116,
21616–21622
58. Bininda-Emonds, O.R.P. (2004) The evolution of supertrees.Trends Ecol. Evol. 19, 315–322
59. Hinchliff, C.E. et al. (2015) Synthesis of phylogeny and taxonomy into a comprehensive tree of life.
Proc. Natl. Acad. Sci. U. S. A. 112, 12764–12769
60. Rosindell, J. and Harmon, L.J. (2012) OneZoom: a fractal explorer for the tree of life. PLoS Biol. 10,
e1001406
61. Uyeda, J.C. and Harmon, L.J. (2014) A novel Bayesian method for inferring and interpreting the
dynamics of adaptive landscapes from phylogenetic comparative data. Syst. Biol. 63, 902–918
62. McMahon, T.A. and Bonner, J.T. (1984) On Size and Life , Scientific American Library
63. Barbieri, M. et al. (2015) Data Resource Profile: The Human Mortality Database (HMD). Int. J.
Epidemiol. 44, 1549–1556
64. Haley, D. (1986) Marine mammals of eastern North Pacific and Arctic waters , Seattle, Wash.: Pacific
Search Press
9
Posted on 25 Jul 2023 — The copyright holder is the author/funder. All rights reserved. No reuse without permission. — https://doi.org/10.22541/au.169029175.51225048/v1 — This a preprint and has not been peer reviewed. Data may be preliminary.
65. McMurray, S.E. et al. (2008) Redwood of the reef: growth and age of the giant barrel sponge Xestospongia
muta in the Florida Keys. Mar. Biol. 155, 159–171
66. Crowther, M.S. and Blacket, M.J. (2003) Biogeography and speciation in the dasyuridae: why are there
so many kinds of dasyurids. InPredators with pouches: the biology of carnivorous marsupials (M. Jones, C.
Dickman, M. Archer, eds), CSIRO publishing
67. Krajewski, C. et al. (2008) The evolution of reproductive strategies in dasyurid marsupials: implications
of molecular phylogeny.Biol. J. Linn. Soc. Lond. 71, 417–435
68. Duncan, W.H. and Duncan, M.B. (2000) Trees of the Southeastern United States , University of Georgia
Press
69. Brown, P.M. (1996) OLDLIST: A database of maximum tree ages.Tree rings, environment, and humanity. Radiocarbon 1996, 727–731
70. Flanary, B.E. and Kletetschka, G. (2005) Analysis of telomere length and telomerase activity in tree
species of various life-spans, and with age in the bristlecone pine Pinus longaeva . Biogerontology6, 101–111
71. Violle, C. et al. (2007) Let the concept of trait be functional! Oikos 116, 882-892.
72. Stearns, S.C. (1992) The evolution of life histories, Oxford University Press.
73. Wright, J. et al. (2018) Life-history evolution under fluctuating density-dependent selection and the
adaptive alignment of pace-of-life syndromes. Biol. Rev. Camb. Philos. Soc. 94, 230–247
74. Capdevila, P. et al. (2020) Longevity, body dimension and reproductive mode drive differences in aquatic
versus terrestrial life-history strategies. Funct. Ecol. 34, 1613–1625
75. Revell, L.J. (2009) Size-correction and principal components for interspecific comparative studies. Evolution 63, 3258–3268
76. Joliffe, I.T. and Morgan, B.J. (1992) Principal component analysis and exploratory factor analysis. Stat.
Methods Med. Res. 1, 69–95
77. Winemiller, K.O. (1989) Patterns of variation in life history among South American fishes in seasonal
environments. Oecologia 81, 225–241
78. D’Andrea, R. et al. (2020) Counting niches: Abundance-by-trait patterns reveal niche partitioning in a
Neotropical forest. Ecology 101, e03019
79. Kessel, S.T. et al. (2018) Divergent migration within lake sturgeon (Acipenser fulvescens ) populations:
Multiple distinct patterns exist across an unrestricted migration corridor. J. Anim. Ecol. 87, 259–273
80. Perry, K.D. et al. (2020) Genome-wide analysis of diamondback moth, Plutella xylostella L., from
Brassica crops and wild host plants reveals no genetic structure in Australia. Sci. Rep. 10, 12047
81. Frelat, R. et al. (2018) Correction: Community ecology in 3D: Tensor decomposition reveals spatiotemporal dynamics of large ecological communities. PLoS One 13, e0196353
82. Costanza, J.K. et al. (2017) An empirical, hierarchical typology of tree species assemblages for assessing
forest dynamics under global change scenarios. PLoS One 12, e0184062
83. O’Meara, B.C. (2012) Evolutionary inferences from phylogenies: A review of methods. Annu. Rev.
Ecol. Evol. Syst. 43, 267–285
84. Freckleton, R.P. (2009) The seven deadly sins of comparative analysis. J. Evol. Biol. 22, 1367–1375
OUTSTANDING QUESTIONS
* Is there a universal characterisation of life histories across the tree of life?
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* Does the fast-slow continuum explain the majority of life-history variation across all taxa? It does in
Tetrapods (especially mammals and birds), which are relatively over-studied, and only in recent years has
the fast-slow continuum been shown to be important in sessile and clonal organisms (vascular plants, corals).
Whether the fast-slow continuum is the major structuring axis of life history variation has not been studied
in most invertebrates other than insects, where the fast-slow continuum was identified [6], but seems to be
less structuring than in tetrapods [7].
* Are other axes of life history variation consistent among taxa? Traits relating to reproductive or developmental tactics have repeatedly emerged as the second most important axis of life history variation. However,
heterogeneity in the set of traits analysed so far prevents us from concluding taxonomic universality.
* What, if any, are the implications of particular choices of data and analytical approaches? Certainly the
choice of multivariate data to analyse, and the availability of particular measures by taxa, will vary. If the
impact of these choices on research outcomes is significant, cognisance of such consequences is of paramount
importance.
* Are there clearly defined clusters and boundaries of life history variation across taxa that occupy distinct
spaces in multidimensional life history trait space? Biomechanical constraints limit the range of covariation
among life history traits [62]. Intuitively, certain life history strategies should not exist if they defy physical
or evolutionary laws. How will human actions and climate change alter these boundaries and shape rates of
extinction/invasion?
TABLE 1 - Comparison of different types of demographic data in the context of life history strategy
comparative analyses.
Data Type
Strengths
Weaknesses
Source(s)
Examples/references
Simple traits, based on expert natural historian knowledge and opinion.
Simple traits, derived from published measurements.
Life cycle models with age- or stage-based schedules of survival (lx ) and reproduction (mx ), e.g., life tables, projection matri
Life history traits derived from life cycle models using algebraic and computational methods.
Selection pressures on traits, describing the “importance” of vital rates to fitness using the derivative of the latter with resp
BOX 1. LIFE HISTORY STRATEGIES
Are carrots (Daucus carota ) similar to blue ringed octopuses (Hapalochlaena lunulata )? They both start life
small, grow fast but few survive to adulthood, produce many offspring in one breeding event at around 1 years
old, and are semelparous . In contrast, humans (Homo sapiens sapiens ) and blue whales (Balaenoptera
musculus ) grow slowly, mature late but are likely to survive to adulthood, usually produce one offspring
every 2-3 years and have remarkably similar lifespans: the oldest known living human, Jeanne Calment,
reached 122 years of age, and blue whales may live up to 110 [64]. The sacred fig tree (Ficus religiosa ) and
giant barrel sponge (Xestospongia muta ) are like carrots and blue ringed octopuses in that they start life
small, are unlikely to survive to adulthood and, once mature, produce many offspring. Xestospongia muta
and F. religiosa are also like humans and blue whales, however, as they are iteroparous over long lifetimes:
one sacred fig “Jaya Sri Maha Bohi” in Sri Lanka is the oldest known human-planted tree, which at around
2,300 years old is similar in age to the oldest known Caribbean giant barrel sponge [65].
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Posted on 25 Jul 2023 — The copyright holder is the author/funder. All rights reserved. No reuse without permission. — https://doi.org/10.22541/au.169029175.51225048/v1 — This a preprint and has not been peer reviewed. Data may be preliminary.
Whilst distantly-related organisms may share similar life history strategies, closely-related organisms can
show remarkably different life histories. The Dasyuridae family, to which the Tasmanian devil (Sarcophilus
harrisii ) belongs, is one of the most diverse marsupial families [66], with dasyurid species showing different
life history strategies, despite being closely related. Maturity occurs at ˜11 months but, while in some species
all individuals die by 12 months old following a single synchronous mating, others reproduce many times
annually and live for several years [67] . Plant life history strategies are often even more labile than animal
strategies: pine trees (Pinus spp.) vary vastly in lifespan, despite having similar morphology and physiology:
the Virginia pine (P. virginiana ) rarely lives over 150 years [68], whereas bristlecone pine (P. longaeva )
hold the record of non-clonal longevity, at 4,850 year old [69]. Selection for varying longevities in pines may
be a result of the differing fire environments [70].
The Tree of Life abounds with examples of distantly related organisms sharing convergent life history strategies, despite divergent body size and lifestyle, and vice versa . Evolutionary ecologists seek to understand,
across broad taxonomic groups, how and why diverse life history strategies, such as those exemplified here,
are distributed across phylogenies, space, and time.
BOX 2. A MODEL LIFE HISTORY: FROM RESOURCE ACQUISITION TO ALLOCATION
AND FITNESS
An organism’s life history strategy is shaped by traits that have a natural hierarchy. The organism’s phenotype determines how the individual acquires resources [71] through morphological, physiological, and
behavioural adaptations. Development describes the allocation of those resources to competing processes:
supporting somatic maintenance vs. supporting the germline vs.development in either [72]. The consequences
of these allocations are life history traits . These traits are characterised by probability distributions of
survival and fertility. As survival and fertility govern the number of individuals in populations, life history
traits govern not just an organism’s fitness but also itsdemography - population size, structure, and dynamics
[1]. Traits at all hierarchical levels covary with, and feed-back on one another, and are subject to constraints
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Posted on 25 Jul 2023 — The copyright holder is the author/funder. All rights reserved. No reuse without permission. — https://doi.org/10.22541/au.169029175.51225048/v1 — This a preprint and has not been peer reviewed. Data may be preliminary.
imposed by evolutionary history, physical laws, bauplan, and the environment [73]. Natural selection acts to
favour life history strategies that maximise the organism’s fitness in its environment, given those constraints
[1].
Trait currencies and their units vary considerably among life history studies. Moreover, these units do not
necessarily correspond with trait types or hierarchies. Physiological traits often measure energyexpenditure
(e.g., metabolic rate). Behavioural traits typically quantify energetic expenditure (e.g., foraging efficiency)
or space usage (e.g. , home range size). However, space units are also common among morphological
traits (e.g., specific root length). Rates of energetic allocation are used to describe resources given to
developmental processes (e.g ., change in body size over time), thus combining energy and time currencies.
Time is commonly used to measure life history traits, whether as durations (e.g ., mean life expectancy),
rates (e.g ., number of offspring per year), or temporal probabilities linked to survival, development, and
reproduction (e.g. , probability of reaching maturity at a given age). Life history traits are often converted
to expectations of life history for populations or species, which is especially necessary where events occur
only once. For example, an individual only dies once, but the aggregate deaths in a population yield the
distribution of survival for the population’s average phenotype, from which we can estimate e.g.mean life
expectancy. Selection on phenotypic, developmental, or life history traits can quantify the trait’s contribution
to fitness (e.g ., selection pressure). Shaded areas on the figure are indicative, but not exhaustive, of common
currencies used at each level and their overlap.
BOX 3. STATISTICAL METHODS FOR COMPARATIVE ANALYSES OF LIFE HISTORIES
A set of measurable, correlated traits can be described using a smaller number of emergent, orthogonal variables representing dominant axes of life history variation, such as the fast-slow continuum. Principal component analysis (PCA) is one common statistical method to achieve this goal [3–5,7,9,26,27,29,30,33,34,74,75].
Although some -largely arbitrary- guidance exists regarding how many dimensions explain meaningful
amounts of variation [48], it is less clear how to compare dominant axes across independent analyses with
data sets comprising different traits, taxa, and sampling methodologies.
It is also possible to explore relationships between two different multivariate data sets (e.g ., climatic and
life history data). Canonical Correlation Analysis (CCA) yields two sets of emergent uncorrelated variables
by calculating axes with highest correlation between variable sets. This approach recognises that dominant
axes of variation (e.g. , fast-slow) may not yield strong relationships with other ecological or evolutionary
processes.
Unlike both PCA and CCA, Factor Analysis (FA) [47,76] treats measured variables as functions of latent
variables, with associated measurement and/or residual error. As FA does not require latent variables to be
uncorrelated, the approach offers solutions to some problems of PCA and CCA [47]. We suggest that FA is
better suited to the testing of hypothetical, rather than data-driven, axes of variation.
Dimension-reduction analyses fit axes through data, rather than measure the multidimensional boundaries
of life history variation. Cluster Analyses (CA) may help understand, after standardising for the speciesspecific ranking on the fast-slow continuum (by usinge.g. generation time), which and why certain life history
strategies do not exist, as much as the clustered patterning of those that do. Hierarchical CA has previously
been used to identify substructure in life history variation [77] and could prove a useful tool to apply much
more widely in comparative life history theory [78–82].
Depending on the researcher’s perspective, a given environmental, phylogenetic, or morphological variable
may drive life history variation, or be a nuisance covariate to deal with statistically [83]. Comparative analyses
must account for the non-independence from shared evolutionary history [9,47]. Phylogenetic methods exist
for PCA [83], but not yet for FA or CA, forcing researchers to use phylogenetically independent contrasts.
Correlates of life history traits, particularly organism size, cause further challenges: including these correlates
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in analyses risks deriving life history axes defined by non-life-history traits. Moreover, using residuals in
multivariate analyses drawn from regressions of life history against body size can introduce statistical biases
[84].
GLOSSARY
- Actuarial (or reproductive ) senescence : Decreases in survival (or reproduction) with age after
maturity.
- Altricial vs. precocial : born helpless and requiring significant parental care vs. born in an advanced
state and able to feed itself and move independently almost immediately.
- Bauplan : the generalised structural body plan that characterises a group of organisms and especially a
major taxon.
- Generation time : mean age of reproduction in a population. Other definitions exist, such as the average
time between two consecutive generations.
- Fast-slow continuum : pattern of species’ life history strategies structured along two extremes: “fast”
species develop fast, reproduce much, and die young, whereas “slow” species develop slowly, reproduce little,
and live a long life. In its original inception, Stearns referred to it as ‘slow-fast’ [36], but here we revert it as
this is currently a more widely used term.
- Life expectancy : the average period that an organism may expect to live in a population.
- Life history trait : key moments along the life cycle of an organism related to its investment on survival,
development, and/or reproduction. Examples include generation time, age at maturity, longevity, etc .
- Life history strategy : the age- and/or stage-specific patterns and timings of events that make up
an organism’s life cycle. Life history strategies are defined by the combination of life history traits (e.g.,
long-lived semelparous).
- Lifetime reproductive output : total number of offspring produced over the lifetime of an individual.
- Retrogression : the ability to regress to a smaller, younger, or less developed stage with time.
- Semelparity vs. iteroparity : reproductive schedule whereby a single (vs. multiple) reproductive event(s)
occurs during the lifecycle of an organism. In fatal semelparity, death occurs right after reproduction.
- Vital rate : Key demographic process that shapes the dynamics of a population. At minimum, these
rates include survival, development (in stage-based models), and reproduction, but can also include dispersal,
dormancy, etc .
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