| Literature DB >> 17878932 |
Thomas J Webb1, Robert P Freckleton.
Abstract
BACKGROUND: Most animal species display Sexual Size Dimorphism (SSD): males and females consistently attain different sizes, most frequently with females being larger than males. However the selective mechanisms driving patterns of SSD remain controversial. 'Rensch's rule' proposes a general scaling phenomenon for all taxa, whereby SSD increases with average body size when males are larger than females, and decreases with body size when females are larger than males. Rensch's rule appears to be general in the former case, but there is little evidence for the rule when females are larger then males. METHODOLOGY/PRINCIPALEntities:
Mesh:
Year: 2007 PMID: 17878932 PMCID: PMC1964802 DOI: 10.1371/journal.pone.0000897
Source DB: PubMed Journal: PLoS One ISSN: 1932-6203 Impact factor: 3.240
Figure 1A. Rensch's rule as it is often represented schematically.
The dashed line is the line of isometry (male size = female size); the solid line represents Rensch's rule, with SSD increasing with size in species with MBSSD, decreasing with size in species with FBSSD. However, this representation also makes the assumption (not stated by Rensch) that in taxa with mixed SSD, those species with FBSSD will be smaller than species with MBSSD. B. An alternative representation of Rensch's rule, with SSD decreasing with size in FBSSD species, increasing in MBSSD species as before, but both MBSSD and FBSSD species can span the full range of sizes present in the group.
Family specific slopes of log(female) on log(male) size (with 95% CIs) for the 30 families in our dataset with ≥10 species.
| Family | No. species | No. species with MBSSD (Proportion of all species) | Correlation (log(m) and log(f)) | Slope |
| Falconidae | 30 | 1 (0.03) | 0.983 | 1.06 (1.00–1.13) |
| Strigidae | 27 | 1 (0.04) | 0.996 | 1.03 (0.99–1.08) |
| Acciptridae | 104 | 4 (0.04) | 0.990 | 0.94 (0.92–0.96) |
| Tinamidae | 25 | 1 (0.04) | 0.979 | 0.99 (0.91–1.07) |
| Scolopacidae | 73 | 6 (0.08) | 0.958 | 1.00 (0.97–1.04) |
| Muscicapidae | 35 | 14 (0.40) | 0.995 | 1.03 (0.97–1.08) |
| Charadriidae | 62 | 27 (0.44) | 0.998 | 0.98 (0.95–1.02) |
| Apodidae | 12 | 6 (0.50) | 0.950 | 0.99 (0.90–1.07) |
| Cuculidae | 14 | 7 (0.50) | 0.990 | 0.83 (0.72–0.94) |
| Funariidae | 14 | 7 (0.50) | 0.996 | 1.00 (0.89–1.10) |
| Caprimulgidae | 11 | 6 (0.55) | 0.989 | 0.92 (0.73–1.10) |
| Glareolidae | 10 | 6 (0.60) | 0.994 | 1.12 (0.95–1.29) |
| Psittacidae | 32 | 20 (0.62) | 0.992 | 0.96 (0.92–1.01) |
| Thamnophilidae | 20 | 13 (0.65) | 0.991 | 1.04 (0.95–1.13) |
| Trochilidae | 159 | 109 (0.69) | 0.980 | 0.86 (0.82–0.91) |
| Tyrannidae | 67 | 49 (0.73) | 0.994 | 0.96 (0.92–0.99) |
| Laridae | 74 | 55 (0.74) | 0.979 | 0.95 (0.92–0.98) |
| Columbidae | 42 | 32 (0.76) | 0.996 | 1.00 (0.95–1.05) |
| Passeridae | 18 | 14 (0.78) | 0.991 | 0.93 (0.64–1.21) |
| Fringillidae | 142 | 113 (0.80) | 0.994 | 0.90 (0.87–0.93) |
| Ardeidae | 19 | 16 (0.84) | 0.996 | 0.92 (0.86–0.98) |
| Rallidae | 38 | 33 (0.87) | 0.974 | 0.94 (0.91–0.98) |
| Picidae | 48 | 43 (0.90) | 0.995 | 0.97 (0.93–1.02) |
| Anatidae | 77 | 70 (0.91) | 0.988 | 0.98 (0.95–1.02) |
| Cracidae | 11 | 10 (0.91) | 0.995 | 0.93 (0.83–1.03) |
| Gruidae | 11 | 10 (0.91) | 0.959 | 0.90 (0.73–1.07) |
| Sylviidae | 22 | 20 (0.91) | 0.986 | 1.01 (0.92–1.09) |
| Odontophoridae | 14 | 13 (0.93) | 0.989 | 0.93 (0.76–1.11) |
| Corvidae | 37 | 35 (0.95) | 0.993 | 0.96 (0.95–1.00) |
| Phasianidae | 43 | 41 (0.95) | 0.997 | 0.88 (0.84–0.92) |
The total number of species is the number of species for which we had data on male and female size.
This is the OLS slope, note that the RMA slope for a family can be obtained by dividing the OLS slope by the correlation coefficient.
Figure 2SSD (defined here as log(female size/male size)) against log(male size) for the 30 avian families in our dataset for which we had body size data for ≥ 10 species.
The dashed horizontal line indicates no scaling of SSD with size. Also shown are OLS estimates of the relationship between SSD and log(male size) for each family; families with >50% FBSSD species are shown as solid lines, those with >50% MBSSD species as dotted lines. Note that this plot is equivalent to plotting log(female size) against log(male size) with the slopes presented in table 1, but it is easier to see differences between families on the SSD scale.
Figure 3The family-specific slope estimates from table 1 plotted against PMB, the proportion of species within a family displaying MBSSD.
The dotted horizontal line indicates isometry. Circles indicate families with PMB <0.5, triangles those with PMB >0.5, the horizontal solid lines are the means of these two groups, and the shaded grey regions are their respective 95% C.I.s. Solid symbols are those families with PMB ≤0.2 or ≥0.8. The size of each symbol is proportional to the number of species in that family for which we had data. Error bars represent the standard error of the family-specific slope estimates, and for clarity are extended only towards a slope of 1. Three families with a PMB of 0.5 are indicated by crosses, and were not included in the above analysis. Also shown (dashed line) is the simple linear regression of family-specific slope on PMB (weighted by the reciprocal of the s.e. of the family-specific slope).
Figure 4SSD against log(male size) for four families with mixed SSD, A. Laridae, B. Tyrannidae, C. Fringillidae, D. Trochilidae.
In each case, species with FBSSD are shown as filled symbols, those with MBSSD as open symbols. We also include three regression lines on each figure. The solid line is the slope across all species, and is significantly negative in each case. The dashed line is the slope for species with FBSSD only, and differs from isometry only in D. The dotted line is for species with MBSSD only, which is significantly negative in all panels except D.
A summary of relationships obtained from the literature between log(male) and log(female) size from a wide range of taxa with predominantly FBSSD or with mixed MBSSD and FBSSD in which data were provided separately for FBSSD and MBSSD species.
| Taxon | N | Slope | Rensch's rule supported? | Source | |
| by the authors | by us | ||||
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| Spiders (Araneomorphae) | 44 (30000); ≥36 | 0.98 (0.74–1.22) | Y | N | 2 |
| Spiders (Araneomorphae) | 13 (30000); 13 | 0.88±0.135 | Y | N | 6 |
| Orb-weaving spiders (Orbiculariae) | 602 (10000); 579 | 0.99±0.017 | - | N | 40 |
| Beetles (Coleoptera) | 58 (>350 000); 52 | 1.01±0.013 | N | N | 6 |
| Ladybird beetles (Coccinellidae) | 37 (5000); 37 | 1.00±0.017 | N | N | 6 |
| Hummingbird flower mites (Ascidae) | 37 (70); 21 | 0.96±0.042 | Y | N | 12 |
| Water striders (Gerridae) | 46 (500); ≥37 | 0.86 (0.80–0.91) | Y | Y | 2 |
| Water striders (Gerridae) | 112 (500); 93 | 0.93±0.020 | Y | Y | 41 |
| Dragonflies (Anisoptera and Zygoptera) | 21 (5572); 11 | 0.97±0.013 | Y | N | 13 |
| Tephritid flies (Tephritidae) | 32 (4352); 24 | 0.91±0.019 | Y | Y | 34 |
| Fruit flies (Drosophilidae) | 72 (4000); 72 | 0.81±0.027 | Y | Y | 6, 42, 43 |
| Diopsid flies (Diopsidae) | 30 (200); 26 | 0.88±0.024 | Y | Y | 44 |
| Sepsid flies (Sepsidae) | 10 (250); 8 | 0.99±0.107 | Y | N | 6 |
| N. American Hydrapsychid caddisflies | 29 (144); 27 | 1.05±0.043 | N | N | 45 |
| Hymenoptera | 20 (115 000); 19 | 0.98±0.017 | N | N | 6 |
| Lepidoptera | 47 (140 000); 37 | 0.92±0.039 | Y | N | 6 |
| Stick insects (Phasmatodea) | 152 (2500); ? | 0.84 | - | - | 34 |
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| Eublepharid geckos (Eublepharidae) | 11 (20); 5 | 0.97±0.032 | Y | N | 15 |
| Colubrid snakes (Colubridae) | 18 (1800); ≥15 | 1.08 (0.95–1.21) | Y | N | 2 |
| Australian Elapid snakes (Elapidae) | 19 (77); ≥16 | 1.09 (0.64–1.54) | Y | N | 2 |
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| Sharks and rays (Chondrithyes) | 102 (890); 86 | 1.00±0.020 | N | N | Webb, Dulvy & Freckleton, unpublished analysis |
| North American minnows (Cyprinidae) | 61 (411); 28 | 0.98±0.022 | - | N | 30 |
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| Tinamous (Tinamidae) | 25 (47); 24 | 1.00±0.020 | N | N | 17 |
| Hummingbirds (Trochilidae) | 154 (330); 36 | 0.92±0.022 | Y | Y | 12 |
| Raptors (Falconiformes) | 22 (306); ≥18 | 1.00 (0.85–1.14) | Y | N | 2 |
| Owls (Strigiformes) | 25 (189); ≥20 | 1.09 (0.98–1.20) | Y | N | 2 |
| Sandpipers (Scolopacidae) | 35 (86); ≥28 | 0.98 (0.83–1.14) | Y | N | 2 |
| Shorebirds (Ciconiiformes) | 102 (345); 47 | 0.99±0.016 | Y | N | 5 |
The three values for N are: the number of species in the study (approximate number of species in the taxonomic or functional group considered); number of species in sample with FBSSD.
We expand upon our reasons for any disagreement in the text.
Taxa are classified in [2] as female-biased if at least 80% of species in the sample had FBSSD.
Estimates of the slope and its 95% C.I. were measured off figure 2 of [2].
The conclusion in [2] that Rensch's rule was a general phenomenon based on a meta-analysis of the taxa listed here as well as taxa with MBSSD and mixed SSD, and so we list them as supporting Rensch's rule in each case; whereas we consider each taxon separately.
Sample sizes given are for all species in which females are larger than males. However, in the analysis we consider only those species in which the female is ≤2 x the size of the male, which is the conventional delimitation of ‘extreme’ SSD in spiders [40]. When females are much larger than males in this group, the correlation between male and female size breaks down, and it is not clear what the appropriate technique for examining scaling in SSD is in such a situation. The sample sizes for the analyses using data from [6] and [40] were therefore 11 and 476 species respectively.
We analyse data for all species-level data given in the appendix to [41]; note that the analyses presented [41] are at the subfamily level, and use data for 209 species of waterstrider. He found evidence for Rensch's rule in 8 of 9 subfamilies with at least 10 species; we too support Rensch's rule for species with FBSSD in the two largest subfamilies, Gerrinae (n = 59, slope = 0.89±0.028, P = 0.0003) and Halobatinae (n = 21, slope = 0.78±0.081, P = 0.0144).
We focus on thorax length from the several morphological measures given in [34].
We have combined data from the three sources cited in the table. For the small number of species occurring in more than one dataset, we took the arithmetic mean size (across datasets) for male and female size. Including source as a factor in the analysis did not substantially affect the estimate of the slope (common slope estimated as 0.86±0.028, significantly <1 with P<0.00001).
We reject Rensch's rule in this case as the P value for the test for a slope significantly different from 1 is 0.0553, but accept that this is only marginally non-significant.
This slope is an unpublished result mentioned in [34], and is the slope of log(male) on log(female) size, i.e. a situation in which Rensch's rule predicts a slope >1.
We focus on body mass from the several morphological measures given in [17].