Trait - Wiley

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APPENDIX S1: Source of genotypes
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Table A1 shows the source lake for each genotype. Clone lines were started from a
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single parthenogenetic female from each lake, ensuring that individuals in each line
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are genetically identical.
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Table A1 Source lake characteristics for the four genotypes of Daphnia pulicaria.
Location
Surface
Lake Clone
(closest city)
Lindsay 2C
Total P (μg/L)
0.1250a
13.7a
8.0b
44°55’ N 76°40’ W
0.155b
26.0b
Mississippi Station, ON
45°08’ N 78°30’ W
Glen GLEN
0.1630d
15.0d
Haliburton, ON
46°28’ N 80°56’ W
Ramsey RAM
7.9520d
20.5d
Sudbury, ON
a
Provided by Nelson Laboratory, Queen’s University, Kingston, ON
Long
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44°32’ N 76°23’ W
Lake Opinicon, ON
Area
Maximum Depth (m)
(km2)
4B
8
b
From Reavie & Smol, 2001.
9
c
From Reavie et al, 2006.
10
d
Provided by Dorset Environmental Science Center (DESC), Dorset, ON
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4.1c
10.3d
11.5d
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APPENDIX S2: Maternal effects
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Since we were interested in studying life-history traits across a range of resources that
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went from near starvation to moderate abundance, there were some resource levels
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where reproduction did not occur (see Results). As such, it was not possible to control
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for maternal effects for all resource levels. To address the issue of maternal effects,
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we conducted two rounds of experiments. In the first round, all offspring used in the
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treatments came from mothers raised at the highest resource level and thus all life-
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history responses include effects due to the difference between maternal and offspring
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resource environment. In the second round, we took offspring from mothers raised at
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resource levels where reproduction occurred and raised these individuals in the same
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environment as their mother. Thus, we were able to compare the influence of maternal
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environment on life-history trait correlations for the four highest resource levels. Note
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that the two experiments were conducted concurrently, and are only distinguished for
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ease of communicating the analyses and results.
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To evaluate whether maternal effects had an influence on correlation
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coefficient, we estimated correlation coefficients for those individual with maternal
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effects, and those without maternal effects (see Methods), which yielded two
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estimates of correlation coefficients for each genotype at the four highest resource
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levels (0.5, 0.42, 0.34, 0.26 mgC/day). Reproduction was insufficient at lower
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resource levels to raise enough individuals with controlled maternal effects. A two-
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factor ANOVA with maternal effects and treatment indicated no significant impact of
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maternal effects on correlation coefficient for any pair of traits (1- correlation:
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F=2.9823, df=1,24, p=0.0970; 1- correlation: F=1.2463, df=1,24, p=0.2753, -
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correlation: F=0.8018, df=1,24, p=0.3794).
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38
2
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APPENDIX S3: Life-history characterization
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Figure S1 Example growth trajectories (circles) and corresponding fit von Bertalanffy
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growth model (lines). Fit maximum growth rate (1) is shown beside each trajectory.
0.407
2.5
0.3882
0.36
0.3287
Length (mm)
2.0
0.2676
1.5
1.0
0
10
20
30
40
50
60
70
Age (days)
42
43
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Figure C2 Correlation between maximum growth rate (1) and the common metric of
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growth at fixed age (Vanni & Lampert 1992, Boersma & Vijverberg 1994), assuming
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instar duration of 2.5 days (Taylor & Gabriel 1993).
3
0.45
Max Growth Rate
0.40
0.35
0.30
0.25
1.2
1.4
1.6
1.8
2.0
2.2
Length at age 9
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48
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50
51
52
4
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APPENDIX S4: Shapiro-Wilk test for normality of life-history traits
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Table D1 Results (p-value) of a Shapiro-Wilk test for normality of each life-history
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trait (1=growth, =reproduction, =age at death). Values less than 0.05 indicate non-
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normality.
Genotype
GLEN
4B
Ramsey
2C
Trait
F=0.04
F=0.08
F=0.16
F=0.26
F=0.34
F=0.42
F=0.5
1
0.472
0.447
0.597
0.903
0.223
0.103
0.023

-
-
0.048
0.029
0.100
0.218
0.157

0.000
0.036
0.520
0.011
0.000
0.159
0.027
1
0.092
0.048
0.105
0.034
0.453
0.489
0.373

-
-
0.000
0.009
0.017
0.445
0.033

0.000
0.000
0.111
0.174
0.185
0.750
0.010
1
0.053
0.137
0.248
0.163
0.690
0.294
0.553

-
-
0.000
0.077
0.026
0.138
0.328

0.000
0.001
0.628
0.082
0.024
0.002
0.000
1
0.017
0.495
0.004
0.046
0.661
0.307
0.212

-
-
0.000
0.000
0.006
0.099
0.377

0.000
0.000
0.004
0.005
0.028
0.011
0.003
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58
59
5
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APPENDIX S5: Growth variation comparison
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We observed growth variation among genetically identical individuals raised in
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carefully controlled environments, which is common in zooplankton experiments (see
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analysis in Ananthasubramaniam et al. 2011). To ensure this was not an artifact of our
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transfer protocol, we compared the growth variance in our experiment to that found in
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the literature. The highest resolved data is found in Lynch (1988), which shows an
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increase in growth variance with incresing age that peaks around 10 days old (Figure
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E1). Converting to a common basis of carbon per day, two of our food levels (0.5 and
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0.42 mgC/day) correspond to the lowest food level studied in Lynch (1988).
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Comparing these two studies, the dynamics of growth variance in our experiments
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follow a very similar age pattern and is quantitatively similar in terms of both peak
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and average variance values (Figure E2).
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73
74
75
76
77
78
79
80
81
82
83
84
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FIGURE E1. Dynamics of growth variance among genetically identical zooplankton
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individuals from Lynch (1988) across nine food levels.
0.05
0.04
Variance
0.03
0.02
0.01
0.00
0
10
20
30
40
Age (days)
87
88
89
90
91
92
93
94
7
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FIGURE E2. Dynamics of the growth variance among genetically identicals
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observed in our experiments. a) Variance dynamics at 0.5 mgC/day for all four
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genotypes (2C: blue, 4B: green, GLEN: yellow, RAMSEY: red) compared to the 0.1
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mg C/day food level from Lynch (1988; dotted). b) Variance dynamics at 0.42
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mgC/day for all four genotypes (2C: blue, 4B: green, GLEN: yellow, RAMSEY: red)
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compared to the 0.8 mg C/day food level from Lynch (1988; dotted).
0.05
a
0.05
0.03
0.03
Variance
0.04
Variance
0.04
b
0.02
0.02
0.01
0.01
0.00
0.00
0
10
20
Age (days)
30
40
0
10
20
30
Age (days)
101
102
103
104
105
106
107
108
109
8
40
110
APPENDIX S6: Proportion reproducing
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Figure F1. Proportion of adults that reproduced before death. Genotypes are shown in
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different colors (red: RAMSEY, yellow: GLEN green: 4B, blue: 2C)
1.0
Proportion Reproducing
0.8
0.6
0.4
0.2
0.0
0.04
0.08
0.16
0.26
0.34
0.42
0.50
Treatment - mgC/vial/day
113
114
115
116
117
118
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APPENDIX S6: Correlation coefficient analysis
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Table G1 Statistical tests of whether the correlation coefficients differ from zero
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(1=growth, 𝜔=reproduction, δ=age at death). Values in the top part of the table are p-
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values from t-tests at each resource level. The next two blocks show if the null
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hypothesis of no difference from zero is rejected (●) or not (◦). The first of these is
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without adjusting the type I error rate, and the second is adjusting using Sidak’s
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correction. Corresponding alpha values shown in parentheses in the first column.
Trait
Correlations
F=0.04
F=0.08
F=0.16
F=0.26
F=0.34
F=0.42
F=0.5
1-
-
-
0.0084
0.0004
0.0077
0.0028
0.0377
1-
0.0122
0.0940
0.357
0.0031
0.0117
0.0017
0.0005
-
-
-
0.391
0.257
0.106
0.0221
0.0392
Trait
Correlations
Significance without adjusting type I error rate
1- (α=0.05)
-
-
●
●
●
●
●
1- (α=0.05)
●
◦
◦
●
●
●
●
- (α=0.05)
-
-
◦
◦
◦
●
●
Trait
Correlations
Significance with adjusting type I error rate
1-
(α=0.0102)
-
-
●
●
●
●
◦
1-
(α=0.0073)
◦
◦
◦
●
◦
●
●
-
(α=0.0102)
-
-
◦
◦
◦
◦
◦
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129
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APPENDIX REFERENCES
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Ananthasubramaniam, B., Nisbet, R.M., Nelson, W.A., McCauley, E. & Gurney,
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W.S.C. (2011) Stochastic growth reduces population fluctuations in Daphnia–algal
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systems. Ecology, 92, 362-372.
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Boersma, M., & Vijverberg, J. (1994) Seasonal variations in the condition of two
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Daphnia species and their hybrid in a eutrophic lake: evidence for food limitation.
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Journal of Plankton Research, 16, 1793-1809.
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Brookfield, J.F.Y. (1984) Measurement of the intraspecific variation in population
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growth rate under controlled conditions in the clonal parthenogen, Daphnia magna.
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Genetica, 63, 161-174.
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De Graff, G. & and Prein, M. (2005) Fitting growth with the von Bertalanffy growth
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function: a comparison of three approaches of multivariate analysis of fish growth in
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aquaculture experiments. Aquaculture Research, 36, 100-109.
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Ebert, D. (1994) A maturation size threshold and phenotypic plasticity of age and size
at maturity in Daphnia magna. Oikos, 69, 309-317.
Lynch, M. (1988) Path analysis of ontogenetic data. Size-Structured Populations (eds
B. Ebenman & L. Persson), pp.29-46. Springer-Verlag, New York.
Noonburg, E.G., Nisbet, R.M., McCauley, E., Gurney, W.S.C., Murdoch, W.W. & de
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Roos, A.M. (1998) Experimental testing of dynamic energy budget models.
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Functional Ecology, 12, 211-222.
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Nisbet, R.M., McCauley, E., Gurney, W.S.C., Murdoch, W.W. & Wood, S.N. (2004)
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Formulating and testing a partially specified dynamic energy budget model.
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Ecology, 85, 3132-3129.
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153
Reavie, E.D. & Smol, J.P. (2001) Diatom-environmental relationships in 64 alkaline
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southeastern Ontario (Canada) lakes: a diatom-based model for water quality
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reconstructions. Journal of Paleolimnology, 25, 25-42.
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Reavie, E.D., Neill, K.E., Little, J.L. & Smol, J.P. (2006) Cultural eutrophication
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trends in three southeastern Ontario lakes: a paleolimnological perspective. Lake and
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Reservoir Management, 22, 44-58.
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Taylor, B.E. & Gabriel, W. (1993) Optimal adult growth of Daphnia in a seasonal
environment. Functional Ecology, 7, 513-521.
Vanni, M.J. & Lampert, W. (1992) Food quality effect on life history traits and fitness
in the generalist herbivore Daphnia. Oecologia, 92, 48-57.
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