1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 Appendix S1 Data sets Data Set A: Anolis marmoratus Basse Terre Guadeloupe. A defined (Malhotra 1992) subset of traits found in Data set B recorded on adult males only. Data Set B: Anolis oculatus Dominica. A defined (Malhotra 1992) set of traits recorded from both males and females, subject to several studies of natural selection and associated fields (Malhotra 1992; Malhotra & Thorpe 1991a,b, 1992, 1997, 1999; Thorpe & Malhotra 1992; Thorpe et al 2004, 2005). Data set C: Anolis roquet complex northwest and central Martinique. A defined (Thorpe et al 2008) set of traits recorded on adult males only, from along specific transects (Thorpe et al 2008, 2010, 1012; Surget-Groba et al. 2012) and the subject of studies of phylogeography, adaptation and speciation (Johansson et al 2008; Ogden & Thorpe 2002; Surget-Groba et al 2012; Thorpe 2005; Thorpe et al 2003, 2008, 2010,). In addition to the traits used in Fig. 4 and Table S1a, the colour pattern traits chevron intensity, A mark on neck black reticulations on trunk, and nonUV white spots on trunk were also recorded (Thorpe et al 2008) (Table S1d). The data set C Martinique sites (Fig 1) are from the publications (Thorpe et al 20101; Surget-Groba 20122) in the table below. Label 21 22 23 24 25 26 27 28 29 30 31 32 Citation 1 Transect site Habitat NW1 III 1 xeric coastal NW2 1 III 5 montane rainforest NW3 1 III 6 montane rainforest NW4 1 IV 1 xeric coastal NW5 1 IV 2 xeric coastal NW6 1 IV 5 montane rainforest NW7 1 IV 6 montane rainforest NW8 2 combined 1 xeric coastal C1 1 III 7 montane rainforest C2 1 IV 7 montane rainforest C3 1 VIII 6 xeric coastal C4 1 VIII 7 xeric coastal Data set D. Anolis roquet complex northwest and central Martinique. A defined (Malhotra 1992) set of traits recorded on adult males and females from scattered localities across all Martinique (Gianassi 1997). Sites used are figured below. Martinique sample sites for data set D (Thorpe & Stenson 2003). Northwest 55 53 19 33 47 8 12 54 38 7 Central 59 37 Southwest South 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 Data set E. Anolis luciae St Lucia. A defined (Malhotra 1992) set of traits recorded on adult males and females from scattered localities across all St Lucia (Gianassi 1997). Data set F. Anolis trinitatis St Vincent. A set of traits (hue, colour pattern, body dimensions, body length, scalation) recorded from males and females from specific localities in St Vincent. The characters were recorded from live specimens under anaesthetic or from high-resolution digital macrophotographs. Hue (proportion of red, green, blue) was recorded from the lateral trunk using Adobe Photoshop. Achromaticity (greyness) was computed from this as conformity/departure from equal RGB scores. For colour pattern, the intensity of chevrons was recorded on an ordinal scale (0-5) using benchmarks. Both hue and colour pattern follow data set C (Thorpe et al 2008). Scalation characters were 1 ventral scales, 2 circum-trunk scales, 3 dorsal scales along body recorded from trunk and 4 neck 5 giving overall number along body as figured below. 49 50 51 52 Body proportions were 1 snout-vent length, 2 jaw (mouth) length, 3 head length, 4 head depth, 5 head width, 6 upper leg length, 7 lower leg length, 8 toe length and 9 dewlap length as figured below. 53 54 55 56 57 58 59 60 61 62 63 64 65 66 67 68 69 Where covariates were significant (SVL) characters were adjusted by ANCOVAR (Thorpe et al 2008). Data set G. Anolis richardii Grenada. A set of traits (hue, colour pattern, body dimensions, body length, scalation) recorded from males and females from specific localities in Grenada. Traits were recorded and treated as for data set F. Data set H. Anolis aeneus Grenada. A set of traits (hue, colour pattern, body dimensions, body length, scalation) recorded from males and females from specific localities in Grenada. Traits were recorded and treated as for data set F. Comparisons are also made with the invasive A. cristatellus and dry island species A. bonairensis and A. blanquillanus. For the Anolis cristatellus (Dominica invasive), two scalation traits were recorded from specific localities in Dominica (Eales et al. 2008, 2010; Malhotra et al. 2007). 70 71 72 73 74 75 76 77 78 79 80 81 82 83 84 85 86 87 88 89 90 91 92 93 94 95 96 97 98 99 100 101 102 103 104 105 106 107 108 109 110 111 112 113 114 115 116 117 118 119 Molecular and phylogenetic methods. Novel DNA sequences were generated by extracting total DNA from anole tail tips using both commercial kits (Qiagen, cat. no. 69506) and previously published methods (Surget Groba et al. 2001). Mitochondrial fragments were then PCR amplified using the primers MTA-S (5'-ATCTCAGCATGATGAAACTTCG-3') and MTF-S (5'-TTTGGTTTACAAGACCAATG-3') (Thorpe et al. 2008) for MT-CYB, and LCO1490 (5'- GGTCAACAAATCATAAAGATATTGG-3') and HCO2198 (5'TAAACTTCAGGGTGACCAAAAAATCA-3') for MT-CO1 (Folmer et. al. 1994). Sanger sequencing was performed by Macrogen Inc. (www.macrogen.com) using both forward and reverse primers. Forward and reverse sequence chromatograms were proof-read and merged, and the resulting sequences aligned and translated to check for unexpected stop codons or frameshift mutations, using the software Codoncode Aligner version 3.5.6 (www.codoncode.com). Sequence alignments for each species (details in table below) were analysed individually using a Bayesian phylogenetic approach in BEAST v.1.7.4 (Drummond et al. 2012). Gene sequences were partitioned into first, second and third codon positions and separate, unlinked substitution models specified for each. jModelTest (Guindon & Gascuel 2003: Posada 2008) was used to select optimal substitution models according to the corrected Akaike Information Criterion (see table below). Several molecular clock models and coalescent tree priors (suitable for dense intraspecific sampling) were tested in order to determine the most appropriate model specifications. Preliminary BEAST runs using uncorrelated lognormal relaxed clocks were conducted and the posterior distributions of parameters describing variation in evolutionary rate examined. These posterior distributions were found to abut zero for all species, thus failing to reject a constant rate of evolution, and so a strict molecular clock model was employed for all species. A uniform prior of 0.5–1% per million years was applied to the per-lineage substitution rate for the complete MT-CYB, sequence (as opposed to codon positions), based on published rates from other squamate lineages (Surget-Groba & Thorpe 2013). Using a similar procedure, we then tested a coalescent tree prior with exponential population growth, and found the posterior distributions of parameters describing variation in population size to exclude zero for all species, thus rejecting constant population sizes over time. The exponential population growth model was therefore retained for all species. Two independent BEAST runs of 2x107 generations were conducted, sampling the MCMC chain every 2000 generations. The maximum clade credibility (MCC) tree topology was selected from the posterior sample of trees and annotated with posterior clade probabilities and node heights equal to the median value from the posterior sample using TreeAnnotator. For MrBayes analyses, a consensus tree was constructed from the post burn-in trees using all compatible groups. The final trees were visualised in FigTree. BEAST trees for A. luciae and A. richardii (which lacked a well-supported primary dichotomy) were compared to trees from an alternative Bayesian approach in MrBayes 3 (Ronquist and Heulsenbeck 2003). A representative of the bimaculatus Series (A. oculatus) was used as outgroup in both cases. MrBayes analyses involved three independent runs each using one cold and three heated chains, and ran for 13x107 generations sampling the MCMC chain every 1000 generations. Tracer v1.5 (http://beast.bio.ed.ac.uk/Tracer) was used to verify convergence and adequate sampling of all parameters, and determine appropriate burn-in (10% in all cases) for each Bayesian analysis. A consensus tree was constructed from the post burn-in trees using all compatible groups. The final trees were visualised in FigTree and exported 120 121 122 123 124 125 126 127 128 129 130 131 132 133 134 135 136 137 138 139 140 for graphics from TreeView. All sequence alignments and tree files have been uploaded to Dryad and novel DNA sequences have been addition uploaded to GenBank. Details of DNA sequence alignments species individuals gene marmoratus 35 MT-CYB bp 1008 CP1 TrNef+I CP2 CP3 HKY+I+G TrN+G downstream - oculatus luciae 37 93 MT-CYB MT-CYB 1068 1001 TrNef+I HKY TrN+I HKY+G GTR+G K80+I HKY - trinitatis 23 MT-CYB 987 TrNef+G HKY+G GTR+G - richardii 45 MT-CYB 1008 HKY/GTR HKY/HKY TN93/GTR - aeneus 38 MT-CYB 966 K80+G HKY - aeneus 38 MT-CO1 657 K80 luciae 93 MT-CYB 1001 HKY/F81 HKY TrN TrN+G/HK Y+G K80+I/K80+I - TrN Legend for above table. “individuals” shows number of individuals sequenced; “gene” indicates the sequenced gene; “bp” shows the length of the sequence alignment analysed, in base-pairs; “CP1”, “CP2”, “CP3” show the substituion models assigned to each codon position for phylogenetic analysis (where both BEAST and MrBayes analyses were performed, the substitution models used in each are shown before and after the forward-slash, respectively); “downstream” shows the substitution model assigned to a short section of sequence downstream of MT-CYB that was analysed in A. oculatus. 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