Introduction
48
Phenology affects how organisms interact with their environment, generating important 49
consequences for their survival and reproduction. As targets of natural selection and 50
determinants of population vital rates, the timing of growth, reproduction, and other phenological 51
traits are crucial to understanding eco-evolutionary dynamics. For example, in sexual outcrossing 52
plants, flowering phenology governs interaction with mutualists (Fenster et al., 2004), 53
antagonists (Strauss & Whittall, 2006) and abiotic factors (Jin et al., 2019). Consequently, plants 54
experience spatial and temporal variation in natural selection on flowering phenology (Kudo, 55
2007), sometimes resulting in the evolution of local adaptation (Anderson et al., 2012; Fitchett et 56
al., 2015; D. W. Inouye, 2022; Panchen, 2022; Panchen & Gorelick, 2017; Prather et al., 2023). 57
As such, flowering phenology is a useful composite trait for investigating evolutionary responses 58
to past and future environmental challenges. 59
Days to first flower (i.e., flowering time) is a simple yet informative metric with which to 60
study the ecology and evolution of phenology in plant populations. For example, latitudinal and 61
altitudinal clines in days to first flower are common to a variety of plant taxa (Alexander et al., 62
2009; Colautti & Lau, 2015; Halbritter et al., 2018), and reciprocal transplant experiments have 63
confirmed that these clines are an important component of local adaptation (Γ
gren & Schemske, 64
2012; Anderson & Gezon, 2015; Colautti & Barrett, 2013; Ensing & Eckert, 2019; Griffith & 65
Watson, 2005). Flowering time clines are consistent with local adaptation models characterized 66
by stabilizing selection within populations but a shift in optimal flowering time along 67
environmental gradients (de Villemereuil et al., 2020; Gauzere et al., 2020; Kirkpatrick & 68
Barton, 1997). In contrast to the prediction of stabilizing selection, empirical measurements of 69
selection suggest that flowering time is often under directional selection within populations 70
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(MunguΓa-Rosas et al., 2011). Moreover, long-term phenology records show a variety of 71
responses to climate change -- from earlier to later to no change in flowering time, depending on 72
the species (Rafferty et al., 2020; Wolkovich et al., 2012). Thus, there appears to be 73
disagreement between theoretical models and empirical observations of geographic clines and 74
local adaptation on the one hand and observed measurements of natural selection and phenotypic 75
changes in natural populations on the other (Austen et al., 2017). Antagonistic selection on traits 76
correlated with the onset of flowering offers one potential resolution to this apparent 77
contradiction. 78
Day of first flowering may trade off with other aspects of flowering phenology such as 79
the shape of the flowering schedule. These other aspects of flowering phenology may not be well 80
represented by flowering time (Newstrom et al. 1994; CaraDonna et al., 2014; B. D. Inouye et 81
al., 2019) but have important effects on reproductive fitness (Fox, 2003). The shape of the 82
flowering schedule can be quantified by metrics analogous to central moments of probability 83
distributions, which include the mean, variance, skew, and kurtosis (Box 1). Not to be confused 84
with the central moments of a statistical population or sample, the analogous characteristics of a 85
flowering schedule quantify temporal variation in relative reproductive investment through time. 86
These characteristics use the same mathematical equations (Table 1) but are not shaped by 87
probabilistic process and therefore may not correlate with onset or duration of flowering (Fig. 88
1A). These metrics have rarely been used in studies of flowering phenology, yet they have the 89
potential to offer a novel perspective on selection and trade-offs affecting the evolution of 90
phenology. 91
Central moments of individual flowering schedules describe the timing and intensity of 92
reproductive investment, and thus are likely to experience strong selection from abiotic or biotic 93
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5
features of the environment. We are not aware of studies quantifying evolutionary divergence of 94
entire flowering schedules among naturally occurring populations, but there are reasons to expect 95
populations to evolve differences. For example, individuals that experience competition for 96
pollinators later in the growing season may benefit from showy inflorescences that enhance 97
pollinator attraction (OβNeil, 1997; Thomson, 1980) and be characterized by a flowering 98
schedule with a more positive skew and longer duration. Herbivores and seed predators can be 99
unpredictable, which may select for a bet-hedging strategy and possibly delay in the onset of 100
flowering (Augspurger, 1981; Elzinga et al., 2007; Wright & Meagher, 2003). These conditions 101
might further result in a longer flowering duration with a higher variance and negative skew in 102
the flowering schedule if late-season ramp-up in flowering is limited by harsh growing 103
conditions at the end of a season. 104
In addition to biotic interactions, flowering schedules are likely to be shaped by abiotic 105
factors that determine the timing and duration of environmental conditions favorable to the 106
development of reproductive organs. Shorter growing seasons typically favour an earlier onset of 107
flowering (Austen & Weis, 2015; Colautti & Barrett, 2013; Griffith & Watson, 2005), and may 108
favour reproduction only within a shorter growing season; this would result in flowering 109
schedules with lower duration and variance. In marginal environments, plants may combine 110
strategies, concentrating flower production into a narrow window but also producing a few 111
flowers over a long timeframe as a bet-hedging strategy (Forrest & Thomson, 2010; Simons, 112
2011; Tufto, 2015), which would produce a long-tailed leptokurtic or skewed flowering 113
schedule. The above examples illustrate the complex ways that biotic interactions and the abiotic 114
environment could shape selection on individual flowering schedules, and how these differences 115
can be quantified using equations developed for probability distributions. 116
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Natural selection acts on phenological schedules of individuals, but variation among 117
individuals within a population affect eco-evolutionary interactions with pollinators, herbivores, 118
and potential mates. Just as individuals have flowering schedules, the aggregated flower 119
production of all individuals within a population can be characterized (Box 1), which could yield 120
emergent properties that are relevant to understanding eco-evolutionary feedbacks. We define 121
emergent properties here as deviations in the aggregate population from the average of individual 122
schedules comprising it (Table 1). For example, a population can have a high aggregate variance 123
but low average individual variance in the flowering schedule if individuals vary in onset and 124
duration of flowering. In cases like this, the central moments of the aggregate flowering schedule 125
show characteristics that are emergent and distinct from the typical individual comprising it (Fig. 126
1). Although emergent properties can arise from adaptive processes acting on individuals, they 127
can also have important ecological consequences for species communities. For example, 128
population aggregate flowering schedules are sometimes positively skewed with an abrupt start 129
and a long tail of flowering (Blionis et al., 2001; Rabinowitz et al., 1981), which may be an 130
adaptation to enhance pollinator visitation to the population (Stemkovski et al., 2023; Thomson, 131
1980). Additionally, strong frequency-dependent selection may concentrate flowering within a 132
narrow but synchronous timeframe to attract more pollinators (Rathcke & Lacey, 1985), 133
increase mating opportunities (Ison & Weis, 2017), or prevent interspecific cross-pollination 134
(Fantinato et al., 2018). Therefore, in pollinator or mate-limited environments, population 135
aggregate flowering schedules may be very similar to the average flowering schedule. Thus, 136
emergent properties (or a lack thereof) have the potential to provide insight into eco-evolutionary 137
processes and ecological consequences of aggregate flowering schedules. 138
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Environmental gradients associated with latitude can be useful for studying phenotypic 139
evolution because selection often varies predictably due to shorter growing seasons and weaker 140
biotic interactions towards polar latitudes (reviewed in Zvereva & Kozlov, 2021). Adaptation 141
along gradual environments is commonly manifested as clines in phenotypic traits that are 142
observable when genetically related individuals are grown in a common garden environment 143
(Olsson & Γ
gren, 2002; Panchen, 2022; Sobral et al., 2013). For example, there is good evidence 144
for the rapid evolution of adaptive flowering time clines in the perennial wetland herb Lythrum 145
salicaria (purple loosestrife) during its invasion of North America. Selection splines (Colautti & 146
Barrett, 2010), trait correlations (Colautti & Barrett, 2011), reciprocal transplants (Colautti & 147
Barrett, 2013), and herbarium records (Wu & Colautti, 2022) collectively support a model of 148
constrained selection in which shorter growing seasons toward the northern range limit favour 149
earlier flowering. In contrast, longer growing seasons in the southern part of the introduced range 150
relax selection on flowering time and favors plants that flower later but grow larger in stature. 151
However, by focusing on the first day of flowering, previous studies have ignored other aspects 152
of the flowering schedule that may be important for understanding adaptation and constraint 153
during evolution and invasion of L. salicaria. 154
Here, we investigate clines in flowering schedules among thirteen populations sampled 155
across ten degrees of latitude in eastern North America and grown in a common garden field 156
study at the Koffler Scientific Reserve north of Toronto, Ontario, Canada. We quantify both 157
individual and population aggregate flowering schedules to address the following questions: (1) 158
How well do common phenological metrics, like the onset and duration of flowering, predict 159
often overlooked features of the flowering schedule such as the variance, skew and kurtosis? (2) 160
Are there latitudinal clines in flowering schedules that are consistent with the adaptive 161
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hypotheses outlined above? Specifically, we predicted that longer growing season lengths, 162
stronger competition for pollinators, and higher rates of herbivory in southern populations will 163
have favoured genotypes with: (i) a longer flowering duration and (ii) a more negative kurtosis 164
with a concentrated peak and rare flowering events far from the average flowering day, but also 165
(iii) an increase in the flowering schedule variance and (iv) a more negative skew with flowering 166
focused later in the schedule. (3) Are there emergent properties of population aggregate 167
flowering schedules that differ from the population average of individual flowering schedules? 168
Because natural selection acts on individual flowering schedules, emergent properties represent 169
(i) potential biases in evolutionary inference when aggregate characteristics are used in place of 170
individual or population average characteristics of flowering schedules, and (ii) ecological 171
phenomena that are shaped by selection and potentially affect herbivore and pollinator 172
communities. 173
174
Acknowledgements
474
The authors thank Z. Burivalova and R. Mackenzie for field assistance, and to E.J. Austen, A.E. 475
Weis and J. Friedman for feedback on the analysis. Funding was provided from NSERC 476
Discovery grants to S.C.H.B. and R.I.C. and to M.N.A. from NSERC CGSM. 477
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22
478
AUTHOR CONTRIBUTIONS 479
M.N.A. led the data analysis with assistance from D.M., S.C.H.B., and R.I.C. The 480
conceptualization and experimental design were developed by S.C.H.B. and R.I.C., and all 481
authors contributed to the manuscript, based on an original draft written by M.N.A. 482
483
DATA AVAILABILITY STATEMENT 484
Raw data and fully reproducible R code for all figures, tables, and statistical analyses are 485
available in the Dryad database (DOI:) 486
487
LITERATURE CITED 488
Γ
gren, J., & Schemske, D. W. (2012). Reciprocal transplants demonstrate strong adaptive 489
differentiation of the model organism Arabidopsis thaliana in its native range. New 490
Phytologist, 194(4), 1112β1122. https://doi.org/10.1111/j.1469-8137.2012.04112.x 491
Alexander, J. M., Edwards, P. J., Poll, M., Parks, C. G., & Dietz, H. (2009). Establishment of 492
parallel altitudinal clines in traits of native and introduced forbs. Ecology, 90(3), 493
612β622. https://doi.org/10.1890/08-0453.1 494
Anderson, J. T., & Gezon, Z. J. (2015). Plasticity in functional traits in the context of climate 495
change: A case study of the subalpine forb Boechera stricta (Brassicaceae). Global 496
Change Biology, 21(4), 1689β1703. https://doi.org/10.1111/gcb.12770 497
Anderson, J. T., Inouye, D. W., McKinney, A. M., Colautti, R. I., & Mitchell-Olds, T. (2012). 498
Phenotypic plasticity and adaptive evolution contribute to advancing flowering 499
phenology in response to climate change. Proceedings of the Royal Society B: 500
.CC-BY-NC-ND 4.0 International licenseavailable under a
was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made
The copyright holder for this preprint (whichthis version posted June 3, 2024. ; https://doi.org/10.1101/2024.05.30.596697doi: bioRxiv preprint
23
Biological Sciences, 279(1743), 3843β3852. 501
https://doi.org/10.1098/rspb.2012.1051 502
Augspurger, C. K. (1981). Reproductive synchrony of a tropical shrub: Experimental studies 503
on effects of pollinators and seed predators in Hybanthus prunifolius (violaceae). 504
Ecology, 62(3), 775β788. https://doi.org/10.2307/1937745 505
Austen, E. J., Jackson, D. A., & Weis, A. E. (2014). Describing flowering schedule shape 506
through multivariate ordination. International Journal of Plant Sciences. 507
https://doi.org/10.1086/673934 508
Austen, E. J., Rowe, L., Stinchcombe, J. R., & Forrest, J. R. K. (2017). Explaining the 509
apparent paradox of persistent selection for early flowering. New Phytologist, 510
215(3), 929β934. https://doi.org/10.1111/nph.14580 511
Austen, E. J., & Weis, A. E. (2015). What drives selection on flowering time? An 512
experimental manipulation of the inherent correlation between genotype and 513
environment: causes of selection on flowering time. Evolution, 69(8), 2018β2033. 514
https://doi.org/10.1111/evo.12709 515
Blionis, G. J., Halley, J. M., & Vokou, D. (2001). Flowering phenology of Campanula on Mt 516
Olympos, Greece. Ecography, 24(6), 696β706. https://doi.org/10.1111/j.1600-517
0587.2001.tb00531.x 518
Blossey, B., & Notzold, R. (1995). Evolution of Increased Competitive Ability in Invasive 519
Nonindigenous Plants: A Hypothesis. Journal of Ecology, 83(5), 887β889. 520
https://doi.org/10.2307/2261425 521
.CC-BY-NC-ND 4.0 International licenseavailable under a
was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made
The copyright holder for this preprint (whichthis version posted June 3, 2024. ; https://doi.org/10.1101/2024.05.30.596697doi: bioRxiv preprint
24
CaraDonna, P. J., Iler, A. M., & Inouye, D. W. (2014). Shifts in flowering phenology reshape a 522
subalpine plant community. Proceedings of the National Academy of Sciences, 523
111(13), 4916β4921. https://doi.org/10.1073/pnas.1323073111 524
Colautti, R. I., & Barrett, S. C. H. (2010). Natural selection and genetic constraints on 525
flowering phenology in an invasive plant. International Journal of Plant Sciences, 526
171(9), 960β971. https://doi.org/10.1086/656444 527
Colautti, R. I., & Barrett, S. C. H. (2011). Population divergence along lines of genetic 528
variance and covariance in the invasive plant Lythrum salicaria in eastern North 529
America. Evolution, 65(9), 2514β2529. https://doi.org/10.1111/j.1558-530
5646.2011.01313.x 531
Colautti, R. I., & Barrett, S. C. H. (2013). Rapid adaptation to climate facilitates range 532
expansion of an invasive plant. Science, 342(6156), 364β366. 533
https://doi.org/10.1126/science.1242121 534
Colautti, R. I., & Lau, J. A. (2015). Contemporary evolution during invasion: Evidence for 535
differentiation, natural selection, and local adaptation. Molecular Ecology, 24(9), 536
1999β2017. https://doi.org/10.1111/mec.13162 537
Colautti, R. I., White, N. A., & Barrett, S. C. H. (2010). Variation of SelfβIncompatibility 538
within Invasive Populations of Purple Loosestrife ( Lythrum salicaria L.) from Eastern 539
North America. International Journal of Plant Sciences, 171(2), 158β166. 540
https://doi.org/10.1086/649023 541
Darwin, C. (1877). The Different Forms of Flowers on Plants of the Same Species. John 542
Murray, Albermarle Street. 543
.CC-BY-NC-ND 4.0 International licenseavailable under a
was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made
The copyright holder for this preprint (whichthis version posted June 3, 2024. ; https://doi.org/10.1101/2024.05.30.596697doi: bioRxiv preprint
25
de Villemereuil, P., Charmantier, A., Arlt, D., Bize, P., Brekke, P., Brouwer, L., Cockburn, A., 544
CΓ΄tΓ©, S. D., Dobson, F. S., Evans, S. R., Festa-Bianchet, M., Gamelon, M., Hamel, S., 545
Hegelbach, J., Jerstad, K., Kempenaers, B., Kruuk, L. E. B., Kumpula, J., Kvalnes, T., 546
β¦ Chevin, L.-M. (2020). Fluctuating optimum and temporally variable selection on 547
breeding date in birds and mammals. Proceedings of the National Academy of 548
Sciences, 117(50), 31969β31978. https://doi.org/10.1073/pnas.2009003117 549
Elzinga, J. A., Atlan, A., Biere, A., Gigord, L., Weis, A. E., & Bernasconi, G. (2007). Time after 550
time: Flowering phenology and biotic interactions. Trends in Ecology & Evolution, 551
22(8), 432β439. https://doi.org/10.1016/j.tree.2007.05.006 552
Ensing, D. J., & Eckert, C. G. (2019). Interannual variation in season length is linked to 553
strong co-gradient plasticity of phenology in a montane annual plant. New 554
Phytologist, 224(3), 1184β1200. https://doi.org/10.1111/nph.16009 555
Fantinato, E., Del Vecchio, S., Giovanetti, M., Acosta, A. T. R., & Buffa, G. (2018). New 556
insights into plants co-existence in species-rich communities: The pollination 557
interaction perspective. Journal of Vegetation Science, 29(1), 6β14. 558
https://doi.org/10.1111/jvs.12592 559
Fenster, C. B., Armbruster, W. S., Wilson, P., Dudash, M. R., & Thomson, J. D. (2004). 560
Pollination syndromes and floral specialization. Annual Review of Ecology, 561
Evolution, and Systematics, 35, 375β403. 562
Fitchett, J. M., Grab, S. W., & Thompson, D. I. (2015). Plant phenology and climate change: 563
Progress in methodological approaches and application. Progress in Physical 564
.CC-BY-NC-ND 4.0 International licenseavailable under a
was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made
The copyright holder for this preprint (whichthis version posted June 3, 2024. ; https://doi.org/10.1101/2024.05.30.596697doi: bioRxiv preprint
26
Geography: Earth and Environment, 39(4), 460β482. 565
https://doi.org/10.1177/0309133315578940 566
Forrest, J., & Thomson, J. D. (2010). Consequences of variation in flowering time within and 567
among individuals of Mertensia fusiformis (Boraginaceae), an early spring 568
wildflower. American Journal of Botany, 97(1), 38β48. 569
https://doi.org/10.3732/ajb.0900083 570
Fox, G. A. (2003). Assortative mating and plant phenology: Evolutionary and practical 571
consequences. Evolutionary Ecology Research, 5(1), 18. 572
Gauzere, J., Teuf, B., Davi, H., Chevin, L.-M., Caignard, T., Leys, B., Delzon, S., Ronce, O., & 573
Chuine, I. (2020). Where is the optimum? Predicting the variation of selection along 574
climatic gradients and the adaptive value of plasticity. A case study on tree 575
phenology. Evolution Letters, 4(2), 109β123. https://doi.org/10.1002/evl3.160 576
Grevstad, F. S. (2006). Ten-year impacts of the biological control agents Galerucella pusilla 577
and G. calmariensis (Coleoptera: Chrysomelidae) on purple loosestrife (Lythrum 578
salicaria) in Central New York State. Biological Control, 39(1), 1β8. 579
https://doi.org/10.1016/j.biocontrol.2006.03.007 580
Griffith, T. M., & Watson, M. A. (2005). Stress avoidance in a common annual: Reproductive 581
timing is important for local adaptation and geographic distribution. Journal of 582
Evolutionary Biology, 18(6), 1601β1612. https://doi.org/10.1111/j.1420-583
9101.2005.01021.x 584
Halbritter, A. H., Fior, S., Keller, I., Billeter, R., Edwards, P. J., Holderegger, R., Karrenberg, 585
S., Pluess, A. R., Widmer, A., & Alexander, J. M. (2018). Trait differentiation and 586
.CC-BY-NC-ND 4.0 International licenseavailable under a
was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made
The copyright holder for this preprint (whichthis version posted June 3, 2024. ; https://doi.org/10.1101/2024.05.30.596697doi: bioRxiv preprint
27
adaptation of plants along elevation gradients. Journal of Evolutionary Biology, 587
31(6), 784β800. https://doi.org/10.1111/jeb.13262 588
Inouye, B. D., EhrlΓ©n, J., & Underwood, N. (2019). Phenology as a process rather than an 589
event: From individual reaction norms to community metrics. Ecological 590
Monographs, 89(2), e01352. https://doi.org/10.1002/ecm.1352 591
Inouye, D. W. (2022). Climate change and phenology. WIREs Climate Change, 13(3), e764. 592
https://doi.org/10.1002/wcc.764 593
Ison, J. L., & Weis, A. E. (2017). Temporal population genetic structure in the pollen pool for 594
flowering time: A field experiment with Brassica rapa (Brassicaceae). American 595
Journal of Botany, 104(10), 1569β1580. https://doi.org/10.3732/ajb.1700210 596
Kirkpatrick, M., & Barton, N. H. (1997). Evolution of a speciesβ range. The American 597
Naturalist, 150(1), 1β23. https://doi.org/10.1086/286054 598
Kudo, G. (2007). Flowering phenologies of animal-pollinated plants: Reproductive 599
strategies and agents of selection. In Ecology and Evolution of Flowers. Oxford 600
University Press, Incorporated. 601
Legendre, L., & Legendre, P. (1983). Numerical Ecology. Elsevier Scientific Publishing 602
Company. 603
MacDougall, A. s., Boucher, J., Turkington, R., & Bradfield, G. e. (2006). Patterns of plant 604
invasion along an environmental stress gradient. Journal of Vegetation Science, 605
17(1), 47β56. https://doi.org/10.1111/j.1654-1103.2006.tb02422.x 606
.CC-BY-NC-ND 4.0 International licenseavailable under a
was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made
The copyright holder for this preprint (whichthis version posted June 3, 2024. ; https://doi.org/10.1101/2024.05.30.596697doi: bioRxiv preprint
28
McGoey, B. V., Hodgins, K. A., & Stinchcombe, J. R. (2020). Parallel flowering time clines in 607
native and introduced ragweed populations are likely due to adaptation. Ecology 608
and Evolution, 10(11), 4595β4608. https://doi.org/10.1002/ece3.6163 609
Molina-Montenegro, M. A., AcuΓ±a-RodrΓguez, I. S., Flores, T. S. M., Hereme, R., Lafon, A., 610
Atala, C., & Torres-DΓaz, C. (2018). Is the Success of Plant Invasions the Result of 611
Rapid Adaptive Evolution in Seed Traits? Evidence from a Latitudinal Rainfall 612
Gradient. Frontiers in Plant Science, 9, 208. 613
https://doi.org/10.3389/fpls.2018.00208 614
Montague, J. L., Barrett, S. C. H., & Eckert, C. G. (2008). Re-establishment of clinal 615
variation in flowering time among introduced populations of purple loosestrife 616
(Lythrum salicaria, Lythraceae). Journal of Evolutionary Biology, 21(1), 234β245. 617
https://doi.org/10.1111/j.1420-9101.2007.01456.x 618
MunguΓa-Rosas, M. A., Ollerton, J., Parra-Tabla, V., & De-Nova, J. A. (2011). Meta-analysis 619
of phenotypic selection on flowering phenology suggests that early flowering plants 620
are favoured. Ecology Letters, 14(5), 511β521. https://doi.org/10.1111/j.1461-621
0248.2011.01601.x 622
Newstrom, L. E., Frankie, G. W., & Baker, H. G. (1994). A new classification for plant 623
phenology based on flowering patterns in lowland tropical rain forest trees at Le 624
Selva, Costa Rica. Biotropica, 26(2) 151-169. 625
Olsson, K., & Γ
gren, J. (2002). Latitudinal population differentiation in phenology, life 626
history and flower morphology in the perennial herb Lythrum salicaria. Journal of 627
.CC-BY-NC-ND 4.0 International licenseavailable under a
was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made
The copyright holder for this preprint (whichthis version posted June 3, 2024. ; https://doi.org/10.1101/2024.05.30.596697doi: bioRxiv preprint
29
Evolutionary Biology, 15(6), 983β996. https://doi.org/10.1046/j.1420-628
9101.2002.00457.x 629
OβNeil, P. (1997). Natural selection on genetically correlated phenological characters in 630
Lythrum salicaria l. (Lythraceae). Evolution, 51(1), 267β274. 631
https://doi.org/10.2307/2410980 632
Panchen, Z. A. (2022). Plant reproductive phenology along an elevation gradient in the 633
extreme environment of the Canadian High Arctic. Plant Ecology & Diversity, 15(5β634
6), 213β226. https://doi.org/10.1080/17550874.2022.2147804 635
Panchen, Z. A., & Gorelick, R. (2017). Prediction of Arctic plant phenological sensitivity to 636
climate change from historical records. Ecology and Evolution, 7(5), 1325β1338. 637
https://doi.org/10.1002/ece3.2702 638
Prather, R. M., Dalton, R. M., barr, billy, Blumstein, D. T., Boggs, C. L., Brody, A. K., Inouye, 639
D. W., Irwin, R. E., Martin, J. G. A., Smith, R. J., Van Vuren, D. H., Wells, C. P., 640
Whiteman, H. H., Inouye, B. D., & Underwood, N. (2023). Current and lagged climate 641
affects phenology across diverse taxonomic groups. Proceedings of the Royal 642
Society B: Biological Sciences, 290(1990), 20222181. 643
https://doi.org/10.1098/rspb.2022.2181 644
Price, T., Kirkpatrick, M., & Arnold, S. J. (1988). Directional selection and the evolution of 645
breeding date in birds. Science, 240(4853), 798β799. 646
https://doi.org/10.1126/science.3363360 647
R Core Team. (2022). R: A language and environment for statistical computing. [Computer 648
software]. R Foundation for Statistical Computing. https://www.R-project.org/ 649
.CC-BY-NC-ND 4.0 International licenseavailable under a
was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made
The copyright holder for this preprint (whichthis version posted June 3, 2024. ; https://doi.org/10.1101/2024.05.30.596697doi: bioRxiv preprint
30
Rabinowitz, D., Rapp, J. K., Sork, V. L., Rathcke, B. J., Reese, G. A., & Weaver, J. C. (1981). 650
Phenological properties of wind- and insect-pollinated prairie plants. Ecology, 651
62(1), 49β56. https://doi.org/10.2307/1936667 652
Rafferty, N. E., Diez, J. M., & Bertelsen, C. D. (2020). Changing climate drives divergent and 653
nonlinear shifts in flowering phenology across elevations. Current Biology, 30(3), 654
432-441.e3. https://doi.org/10.1016/j.cub.2019.11.071 655
Rathcke, B., & Lacey, E. P. (1985). Phenological patterns of terrestrial plants. Annual 656
Review of Ecology and Systematics, 16(1), 179β214. 657
https://doi.org/10.1146/annurev.es.16.110185.001143 658
Rausher, M. D. (1992). The measurement of selection on quantitative traits: Biases due to 659
environmental covariances between traits and fitness. Evolution, 46(3), 616β626. 660
https://doi.org/10.1111/j.1558-5646.1992.tb02070.x 661
RStudio Team. (2022). RStudio: Integrated Development for R [Computer software]. 662
RStudio, PBC. http://www.rstudio.com/. 663
Samis, K. E., Murren, C. J., Bossdorf, O., Donohue, K., Fenster, C. B., Malmberg, R. L., 664
Purugganan, M. D., & Stinchcombe, J. R. (2012). Longitudinal trends in climate drive 665
flowering time clines in North American Arabidopsis thaliana. Ecology and 666
Evolution, 2(6), 1162β1180. https://doi.org/10.1002/ece3.262 667
Simons, A. M. (2011). Modes of response to environmental change and the elusive 668
empirical evidence for bet hedging. Proceedings of the Royal Society B: Biological 669
Sciences, 278(1712), 1601β1609. https://doi.org/10.1098/rspb.2011.0176 670
.CC-BY-NC-ND 4.0 International licenseavailable under a
was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made
The copyright holder for this preprint (whichthis version posted June 3, 2024. ; https://doi.org/10.1101/2024.05.30.596697doi: bioRxiv preprint
31
Sobral, M., GuitiΓ‘n, J., GuitiΓ‘n, P., & Larrinaga, A. R. (2013). Selective pressure along a 671
latitudinal gradient affects subindividual variation in plants. PLOS ONE, 8(9), 672
e74356. https://doi.org/10.1371/journal.pone.0074356 673
Sokal, R. R., & Rohlf, F. J. (1995). Biometry (3rd ed.). WH Freeman. 674
Stemkovski, M., Dickson, R. G., Griffin, S. R., Inouye, B. D., Inouye, D. W., Pardee, G. L., 675
Underwood, N., & Irwin, R. E. (2023). Skewness in bee and flower phenological 676
distributions. Ecology, 104(1), e3890. https://doi.org/10.1002/ecy.3890 677
Strauss, S. Y., & Whittall, J. B. (2006). Non-pollinator agents of selection on floral traits. In 678
Ecology and Evolution of Flowers (pp. 120β135). Oxford Biology. 679
Thomson, J. D. (1980). Skewed flowering distributions and pollinator attraction. Ecology, 680
61(3), 572β579. https://doi.org/10.2307/1937423 681
Tufto, J. (2015). Genetic evolution, plasticity, and bet-hedging as adaptive responses to 682
temporally autocorrelated fluctuating selection: A quantitative genetic model. 683
Evolution, 69(8), 2034β2049. https://doi.org/10.1111/evo.12716 684
Urbanski, J., Mogi, M., OβDonnell, D., DeCotiis, M., Toma, T., & Armbruster, P. (2012). Rapid 685
Adaptive Evolution of Photoperiodic Response during Invasion and Range 686
Expansion across a Climatic Gradient. The American Naturalist, 179(4), 490β500. 687
https://doi.org/10.1086/664709 688
van Kleunen, M., Bossdorf, O., & Dawson, W. (2018). The ecology and evolution of alien 689
plants. Annual Review of Ecology, Evolution, and Systematics, 49(1), 25β47. 690
https://doi.org/10.1146/annurev-ecolsys-110617-062654 691
.CC-BY-NC-ND 4.0 International licenseavailable under a
was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made
The copyright holder for this preprint (whichthis version posted June 3, 2024. ; https://doi.org/10.1101/2024.05.30.596697doi: bioRxiv preprint
32
Waites, A. R., & Γ
gren, J. (2006). Stigma receptivity and effects of prior self-pollination on 692
seed set in tristylous Lythrum salicaria (Lythraceae). American Journal of Botany, 693
93(1), 142β147. https://doi.org/10.3732/ajb.93.1.142 694
Wolkovich, E. M., Cook, B. I., Allen, J. M., Crimmins, T. M., Betancourt, J. L., Travers, S. E., 695
Pau, S., Regetz, J., Davies, T. J., Kraft, N. J. B., Ault, T. R., Bolmgren, K., Mazer, S. J., 696
McCabe, G. J., McGill, B. J., Parmesan, C., Salamin, N., Schwartz, M. D., & Cleland, 697
E. E. (2012). Warming experiments underpredict plant phenological responses to 698
climate change. Nature, 485(7399), Article 7399. 699
https://doi.org/10.1038/nature11014 700
Wright, J. W., & Meagher, T. R. (2003). Pollination and seed predation drive flowering 701
phenology in Silene latifolia (Caryophyllaceae). Ecology, 84(8), 2062β2073. 702
https://doi.org/10.1890/02-0676 703
Wu, Y., & Colautti, R. I. (2022). Evidence for continent-wide convergent evolution and 704
stasis throughout 150 y of a biological invasion. Proceedings of the National 705
Academy of Sciences, 119(18), e2107584119. 706
https://doi.org/10.1073/pnas.2107584119 707
Zvereva, E. L., & Kozlov, M. V. (2021). Latitudinal gradient in the intensity of biotic 708
interactions in terrestrial ecosystems: Sources of variation and differences from the 709
diversity gradient revealed by meta-analysis. Ecology Letters, 24(11), 2506β2520. 710
https://doi.org/10.1111/ele.13851 711
712
.CC-BY-NC-ND 4.0 International licenseavailable under a
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Box 1: Summary characteristics of flowering schedules
Central moments (i.e., mean, variance, skew, and kurtosis) arise from probability theory and
characterize distributions that can be visualized as histograms with observed values on the x-axis
and probability density, frequency, or number of observations on the y-axis. Here, we use the
same equations to describe analogous characteristics of flowering schedules that arise from
developmental rather than probabilistic process. In contrast to probability histograms, flowering
schedules can be visualized as a time series with number or proportion of flowers on the y-axis.
Although the underlying processes are distinct, the equations are the same (Table 1). To
understand the biological significance of mean, variance, skew and kurtosis, we contrast
flowering schedules of different shape (Fig. 1). Standardizing to proportion of open flowers (P
t)
over time (t), rather than total flower number (Nt) accounts for variation in total flower number.
Moreover, we can use proportions to calculate a weighted mean day of flowering. By analogy to
the mean of a probability distribution, the weighted mean of a flowering schedule represents the
βbalance pointβ, which better captures the anthesis day of a typical flower.
As demonstrated in Figure 1A, central moments capture biologically meaningful
variation in flowering schedules that may not be correlated with onset or duration of flowering.
For example, the variance parameter (ππ
ππ
2) describes how much flowering is spread out, even if
the start and end dates are the same. An individualβs coefficient of skew (CSi) accounts for
expected differences in variance and thus describes whether flowering is concentrated earlier
(i.e., right skew, CSi > 0 as shown by the blue dashed line) or later in the schedule (i.e., left skew,
CSi < 0 as shown by the purple dotted line). Finally, the coefficient of kurtosis (CKi) describes
deviations from the Gaussian expectation, contrasting individuals with a concentrated cluster of
open flowers and a few flowers over a long-time frame (i.e., leptokurtic distribution, CKi > 0 as
shown in the gold dashed line) or individuals that spread out flowering more evenly over the
entire schedule (i.e., platykurtic, CKi < 0 as shown by the dashed green line). In addition to
calculating these characteristics for individual plants, all flowers (or proportion of flowers) on
each day can be pooled to yield a population aggregate flowering schedule (Fig. 1B). The
aggregate schedule of a population may not be representative of the individual schedules
comprising it, resulting in emergent properties that we define as deviations from the average
individual flowering schedule.
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Table 1. Equations of flowering schedule characteristics for an average individual within each
population and for the aggregate population of pooled individuals.
Summary Statistic Individual (i) Population aggregate (j)
Proportion (ππ) of flowers (πΉπΉ)
produced at time π‘π‘ ππππ,π‘π‘= πΉπΉππ,π‘π‘
β πΉπΉππ,π‘π‘ π‘π‘
πππ‘π‘,ππ
β =
πΉπΉπ‘π‘,ππ
β
β πΉπΉπ‘π‘,ππ
β
π‘π‘
=
β πΉπΉππ,π‘π‘,ππ ππ
β β πΉπΉππ,π‘π‘,ππ ππ π‘π‘
Day of first flower πΌπΌππ= min{π‘π‘ β£ πΉπΉππ,π‘π‘> 0} πΌπΌππ
β = min{π‘π‘ β£ οΏ½ πΉπΉππ,π‘π‘,ππ
ππ
> 0}
Day of last flower πΊπΊππ= max{π‘π‘ β£ πΉπΉππ,π‘π‘> 0}
πΊπΊππ
β = max{π‘π‘ β£ οΏ½ πΉπΉππ,π‘π‘,ππ
ππ
> 0}
Duration of flowering πΊπΊππβ πΌπΌππ
πΊπΊππ
β β πΌπΌππ
β
Day of mean flowering ππππ= οΏ½ π‘π‘
π‘π‘
ππππ,π‘π‘
ππππ
β = οΏ½ π‘π‘
π‘π‘
πππ‘π‘,ππ
β
Flowering schedule variance ππππ
2 = οΏ½ (π‘π‘ β ππ)2
π‘π‘
πππ‘π‘
ππππ
2β = οΏ½ οΏ½π‘π‘ β ππππ
βοΏ½
2
π‘π‘
πππ‘π‘,ππ
β
Flowering schedule coefficient of
skew πΆπΆππππ= β (π‘π‘ β ππππ)3
π‘π‘ ππππ,π‘π‘
ππππ
3
πΆπΆππππ=
β οΏ½π‘π‘ β ππππ
βοΏ½
3
π‘π‘ πππ‘π‘,ππ
β
ππππ
3β
Flowering schedule coefficient of
kurtosis πΆπΆπΎπΎππ= β (π‘π‘ β ππππ)4
π‘π‘ ππππ,π‘π‘
ππππ
4 β 3
πΆπΆπΎπΎππ=
β οΏ½π‘π‘ β ππππ
βοΏ½
4
π‘π‘ πππ‘π‘,ππ
β
ππππ
4β
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Table 2. Summary of the first five eigenvector axes of a Principal Coordinates Analysis (PCoA)
using Kolmogorov-Smirnov distances between flowering schedules of 369 plants from 13
populations of Lythrum salicaria sampled along a latitudinal gradient and grown in a common
garden at the Koffler Scientific Reserve in Newmarket, ON. Percent variation is calculated as the
eigenvalue over the sum of all positive eigenvalues.
Axis Eigenvalue Variation
explained (%)
PCoA1 13.4 23.5
PCoA2 6.6 11.5
PCoA3 3.9 6.9
PCoA4 3.2 5.6
PCoA5 2.6 4.7
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Table 3. Standardized slope and test statistics of univariate linear regressions testing latitude as a
predictor of the bootstrapped means of average and aggregate population flowering schedule
traits, and the emergent property (i.e. population aggregate minus average) in populations of
Lythrum salicaria. Bold text indicates significant values.
Linear term Quadratic term
Traits Ξ² F (1,11) P X2 P
Start
Average -0.856 30.0 < 0.001 1.73 0.189
Aggregate -0.591 5.92 < 0.05 0.01 0.907
Emergent 0.857 30.52 < 0.001 2.50 0.114
Duration Average -0.369 1.73 0.215 0.11 0.738
Aggregate -0.849 28.37 < 0.001 0.01 0.904
Emergent -0.470 3.13 0.105 2.96 0.085
Mean
Average -0.881 38.0 < 0.001 0.47 0.494
Aggregate -0.845 27.5 < 0.001 0.12 0.724
Emergent 0.368 1.66 0.224 0 0.948
Variance Average 0.031 0.01 0.920 0.07 0.791
Aggregate -0.214 0.53 0.483 0 0.977
Emergent 0.156 0.276 0.610 6.83 < 0.01
Skew Average 0.745 13.7 < 0.01 1.03 0.310
Aggregate 0.382 1.87 0.198 0.07 0.797
Emergent 0.227 0.60 0.456 0.12 0.741
Kurtosis Average -0.590 5.88 < 0.05 0.20 0.659
Aggregate -0.592 5.94 < 0.05 0.88 0.347
Emergent -0.133 0.19 0.664 1.18 0.279
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Figure 1. Hypothetical flowering schedules of (A) five individuals with different characteristics
and (B) their pooled aggregate flowering schedule. Flowering schedules are scaled to the
proportion of total flower production (P
t) over time (t).
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Figure 2. Matrices showing pairwise Pearson correlation coefficients among the start, duration,
central moments (i.e., variance, skew and kurtosis), and two the first two eigenvectors of a
principal coordinates analysis (PCoA) characterizing flowering schedules in populations of
Lythrum salicaria grown in a common garden. The metrics were calculated using either (A)
flowering schedule characteristics averaged across individuals within each population (n = 13),
(B) the residual correlations calculated on deviations of individuals from their population means
(n = 369), or (C) aggregated schedules for individuals pooled within populations (n = 13).
Circles are shown for statistically significant correlations (p < 0.05), colour-coded by correlation
coefficient (i.e., -1 to 1 as shown on the x-axis).
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Figure 3. Principal Coordinates Analysis (PCoA) of Kolmogorov-Smirnov distances between
flowering schedules of 369 plants from 13 populations of Lythrum salicaria sampled along a
latitudinal gradient and grown in a common garden at the Koffler Scientific Reserve in
Newmarket, ON. Point colors correspond to latitude of origin, ranging from dark (48Β° N) to light
(38Β° N). Bar plots show representative flowering schedules of four individual plants. PCoA1 is
inversely related to the central moments of variance and mean such that points on the right
represent individuals with lower flowering schedule variance and an earlier peak.
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Figure 4. Bivariate plots showing relations between latitude and flowering schedule
characteristics of 13 populations of Lythrum salicaria grown in a common garden field
experiment. The bootstrapped estimate and 95% confidence intervals of average individual
flowering schedule characteristics are shown for each population along the left column. The
bootstrapped estimate and 95% confidence intervals of the aggregate flowering schedules for all
flowers within each population are shown in the middle column. The right column indicates the
βemergent propertiesβ of each population, defined as the aggregate minus the average.
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Appendix S1. The distribution of 369 individuals and 216 seed families representing 13
populations of Lythrum salicaria sampled along a latitudinal gradient and grown in a common
garden at the Koffler Scientific Reserve in Newmarket, ON. Point colors correspond to latitude
of origin ranging from dark (48Β° N) to light (38Β° N).
Latitude (Β°) Number of seed
families
Number of
individuals
38.75261 15 23
40.34025 15 33
41.31283 18 24
42.23822 20 34
42.52306 12 34
43.69719 19 21
44.49339 19 38
44.59489 19 22
45.26278 16 26
45.43194 17 36
45.49000 16 23
47.69081 14 32
48.47892 16 23
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FIGURE LEGENDS
Figure 1. Hypothetical flowering schedules of (A) five individuals with different characteristics
and (B) their pooled aggregate flowering schedule. Flowering schedules are scaled to the
proportion of total flower production (Pt) over time (t).
Figure 2. Matrices showing pairwise Pearson correlation coefficients among the start, duration,
central moments (i.e., variance, skew and kurtosis), and two the first two eigenvectors of a
principal coordinates analysis (PCoA) characterizing flowering schedules in populations of
Lythrum salicaria grown in a common garden. The metrics were calculated using either (A)
flowering schedule characteristics averaged across individuals within each population (n = 13),
(B) the residual correlations calculated on deviations of individuals from their population means
(n = 369), or (C) aggregated schedules for individuals pooled within populations (n = 13).
Circles are shown for statistically significant correlations (p < 0.05), colour-coded by correlation
coefficient (i.e., -1 to 1 as shown on the x-axis).
Figure 3. Principal Coordinates Analysis (PCoA) of Kolmogorov-Smirnov distances between
flowering schedules of 369 plants from 13 populations of Lythrum salicaria sampled along a
latitudinal gradient and grown in a common garden at the Koffler Scientific Reserve in
Newmarket, ON. Point colors correspond to latitude of origin, ranging from dark (48Β° N) to light
(38Β° N). Bar plots show representative flowering schedules of four individual plants. PCoA1 is
inversely related to the central moments of variance and mean such that points on the right
represent individuals with lower flowering schedule variance and an earlier peak.
Figure 4. Bivariate plots showing relations between latitude and flowering schedule
characteristics of 13 populations of Lythrum salicaria grown in a common garden field
experiment. The bootstrapped estimate and 95% confidence intervals of average individual
flowering schedule characteristics are shown for each population along the left column. The
bootstrapped estimate and 95% confidence intervals of the aggregate flowering schedules for all
flowers within each population are shown in the middle column. The right column indicates the
βemergent propertiesβ of each population, defined as the aggregate minus the average.
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