Dissolving the plastics problem.

Background: The mosquito Culex annulirostris Skuse (Diptera: Culicidae) is the major vector of endemic arboviruses in Australia and is also responsible for the establishment of the Japanese encephalitis virus (JEV) in southern Papua New Guinea (PNG) as well as its incursions into northern Australia. Papua New Guinea and mainland Australia are separated by a small stretch of water, the Torres Strait, and its islands. While there has been regular JEV activity on these islands, JEV has not established on mainland Australia despite an abundance of Cx. annulirostris and porcine amplifying hosts. Despite the public health significance of this mosquito and the fact that its adults show overlapping morphology with close relative Cx. palpalis Taylor, its evolution and genetic structure remain undetermined. We address a hypothesis that there is significant genetic diversity in Cx. annulirostris and that the identification of this diversity will shed light on the paradox that JEV can cycle on an island 70 km from mainland Australia while not establishing in Australia itself. Results: We sequenced 538 bp of the mitochondrial DNA cytochrome oxidase I gene from 273 individuals collected from 43 localities in Australia and the southwest Pacific region to describe the phylogeography of Cx. annulirostris and its sister species Cx. palpalis. Maximum Likelihood and Bayesian analyses reveal supporting evidence for multiple divergent lineages that display geographic restriction. Culex palpalis contained three divergent lineages geographically restricted to southern Australia, northern Australia and Papua New Guinea (PNG). Culex annulirostris contained five geographically restricted divergent lineages, with one lineage restricted to the Solomon Islands and two identified mainly within Australia while two other lineages showed distributions in PNG and the Torres Strait Islands with a southern limit at the top of Australia's Cape York Peninsula. Conclusion: The existence of divergent mitochondrial lineages within Cx. annulirostris and Cx. palpalis helps explain the difficulty of using adult morphology to identify Cx. annulirostris and its ecological diversity. Notably, the southern limit of the PNG lineages of Cx. annulirostris coincides exactly with the current southern limit of JEV activity in Australasia suggesting that variation in these COI lineages may be the key to why JEV has not yet established yet on mainland Australia. Published: 29 June 2007 BMC Evolutionary Biology 2007, 7:100 doi:10.1186/1471-2148-7-100 Received: 31 October 2006 Accepted: 29 June 2007 This article is available from: http://www.biomedcentral.com/1471-2148/7/100 © 2007 Hemmerter et al; licensee BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/2.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.


Background
Northern Australia has the ideal conditions for the establishment of the Japanese encephalitis virus (JEV), given its dual abundance of both Culex annulirostris Skuse -a vector identified as transmitting JEV in the region [1,2] -and the feral pig populations that act as principal amplifying hosts for the virus's transmission to humans [3]. Over the last decade JEV has become endemic in Papua New Guinea (PNG), and now cycles yearly on islands in the Torres Strait 70 km from mainland Australia (see Figure 1; [4]). It has appeared twice on Australia's Cape York since 1998, but in each case the virus did not establish [4,5].
Given these conditions, the failure of JEV to establish itself on the Australian continent over the past decade has perplexed researchers. Suggested explanations for this have included the presence of alternative blood-meal hosts and competition with antigenically related arboviruses for susceptible vertebrate hosts [5]. But another possibility is that unrecognized species or population variation of this vector throughout southern PNG and northern Australia itself may limit the establishment of JEV. Are there differences between the Cx. annulirostris populations that exist where JEV occurs in PNG and the Torres Strait, and in mainland Australia that work to contain rather than spread JEV throughout this region? As this first unravelling of the genetic diversity of this species and its closely related sister species suggests, population variation around the southern limit of JEV may in fact restrict the movement of an arbovirus.
Although mosquitoes are the vectors of pathogens that cause significant human disease, their genetic diversity remains poorly understood. In our region of Australasia (Australia and the southwest Pacific) the closely related mosquito species Cx. annulirostris, Cx. palpalis Taylor and the coastally restricted Cx. sitiens Wiedemann are abundant with distributions in Australia, Papua New Guinea (PNG) and the Solomon Islands [6]. The morphospecies Cx. annulirostris transmits exotic JEV and is also Australia's principal vector of endemic arboviruses that cause human disease, including Ross River virus, Barmah Forest virus, Murray Valley encephalitis virus and Kunjin virus (a subtype of West Nile Virus) [1,3,[7][8][9]]. The potential establishment of JEV in northern Australia is of serious concern to public health officials in Australia [9], as this virus, which was restricted to Southeast Asia, is responsible for an estimated 30,000-50,000 cases there annually [10]. Yet despite regular JEV activity in the Torres Strait and seroconversions of sentinel animals in 1998 and 2002 on Australia's Cape York, there is no evidence that JEV has become enzootic on the Australian mainland [5].
Overlapping morphology exists between these Culex taxa and allozyme and PCR-based procedures, previously developed to separate these mosquitoes, have suggested the presence of cryptic species within these morphospecies [11,12]. In this study we have sequenced the cytochrome oxidase subunit I gene (COI) to look at the genetic structure, evolution and distribution of Cx. annulirostis, Cx. palpalis and Cx. sitiens collected in Australasia. We evaluate this DNA barcoding marker in a phylogenetic framework to examine the genetic diversity of three Culex morphospecies, one of which is the most important arbovirus vector in Australasia.
We present sequence data generated from 273 mosquitoes that support the distinction of the three morphospecies, as well as the recognition of multiple divergent lineages. The phylogeographic pattern is most complex in Cx. annulirostris with two distinct paraphyletic lineages recognized within Australia -both independently related to the PNG lineages. This data provides phylogenetic support for a recent historical connection of mosquito populations in Australia and PNG that will facilitate more rational arbovirus competency experiments and better surveillance for these mosquitoes in the future. Importantly, the southern limit of the two PNG Cx. annulirostris lineages equates exactly to the current southern limit of JEV activity in the Australasian region.

Mosquito identification: morphology versus rDNA ITS1 and COI
There was 10% incongruity between the ITS1 diagnostic results and the morphology of 218 field collected adults (see Additional file 1). For Cx. annulirostris, correct morphological identification occurred 95.6% of the time (8 individuals out of 180 were incorrectly identified as Cx. palpalis), 95.5% for Cx. sitiens (1 out of 22 individuals was incorrectly identified as Cx. annulirostris) and 62.5% for Cx. palpalis (14 of 40 were incorrectly identified as Cx. annulirostris and one as Cx. sitiens). These results confirm the difficulty distinguishing Cx. palpalis from Cx. annulirostris and highlight the fact that Cx. palpalis is probably underrepresented in studies that use morphology only for species discrimination.
Of 182 different COI haplotypes found in 273 field-collected mosquitoes -comprising 28 Cx. sitiens, 208 Cx. annulirostris and 37 Cx. palpalis -there was 100% agreement between the ITS1 diagnostic and the COI sequence grouping of Culex spp. The final sequence alignment (see Additional file 3) was 538 nucleotides of which 77% (414 nt) were constant, 19% (100 nt) were parsimony informative and the remaining 4% (24 nt) represented unique singletons. The majority (89%) of the parsimony informative sites were detected at the 3rd codon position, compared with 11% at the 1st codon position and none in the 2nd position. A pronounced AT-bias was observed at the 3rd codon position and when the three codons were examined separately, differences in nucleotide compositions were observed. For example, at the first codon position, guanine was represented 30.6% of the time, compared to 15.7% in the second codon position and 2.4% in the third codon position, suggesting that significant differences in the model of sequence evolution between three codon positions are required. To counterbalance the effect of discrepancy between codon position and nucleotide diversity, a GTR model (which allows for the variation of base frequencies and unique probability for each of the six possible substitution classes) was selected in agreement with ModelTest 3.6 [13] for the Maximum Likelihood analyses. The complex model of substitution including gamma distribution and invariant sites (GTR+Γ+I) was selected for the full alignment by the hierarchical likelihood ratio test (LRT) as well as the Akaike information criterion (AIC). Moreover, the dataset for the Bayesian analysis was separated into partitions corresponding to first, second and third codon positions, thus allowing application of independent parameters for these partitions in order to better fit the model to the dataset.
The translation of the nucleotide sequence into an amino acid sequence, using the invertebrate genetic code, showed identical amino acid sequences for all considered haplotypes in the three species, except for a single amino acid valine substituted to leucine in haplotype a126 (DQ673707) of Cx. annulirostris collected in PNG. Both valine and leucine are similar in their chemical properties, being non-charged and hydrophobic. This mutation has been verified using three independent PCR amplifications and direct bidirectional sequencing.  Table 1, Supplementary see Additional file 1 and 2). Pie chart graphs indicate the distributional frequency of Cx. annulirostris haplotypes representing the five identified mtDNA COI lineages. The size of the pie charts' segments is proportional to the number of mosquitoes identified as Cx. annulirostris, which is also indicated in brackets. Haplotype a51 from the laboratory colony at AMI in Queensland, Australia, is not included. (B) Summarized Bayesian phylogenetic tree. Phylogenetic tree of Cx. annulirostris showing 134 COI haplotypes compressed into the 5 different lineages of Cx. annulirostris. Branch support is Bayesian posterior probability/ML bootstraps (expanded in Figure 2). Haplotypes belonging to Cx. sitiens were used as an outgroup. Both the Maximum Likelihood and Bayesian methods show that the COI was able to discriminate the three taxa and confirmed all ITS1 identifications as well as several divergent lineages within Cx. annulirostris and Cx. palpalis ( Figure 2 and see Additional file 1). Both phylogenetic methods produced the same tree with Maximum Likelihood showing lower branch support.
Culex sitiens was the most divergent taxon, showing little geographic structure; the same haplotypes (s9, s8) occurred on both the east and west coasts of Australia. The haplotypes (s11-s14) from PNG do form a clade within the Australian grouping (s1-10, s15), but as only 26 individuals were assessed little can be interpreted from this.
Both phylogenetic methods support the division of Cx. palpalis into three divergent lineages (pal-N-AUS, pal-S-AUS and pal-PNG) that show no geographic overlap (see Additional file 2). The pal-PNG lineage was restricted to PNG and the Torres Strait; the pal-N-AUS lineage was restricted to northern Australia; and the pal-S-AUS was found only in southern Australia.
Culex annulirostris comprised four distinct lineages (ann-PNG1, ann-SI, ann-S-AUS and ann-AUS) with a fifth sublineage identified within the ann-AUS lineage (ann-PNG2) in Figures 1 and 2 due partly to the restricted distribution of this clade, which is the same as ann-PNG1. These lineages showed clear geographic structure ( Figure  1). The ann-AUS lineage exists throughout Australia and southern PNG while the ann-S-AUS lineage appears to be more abundant in southern Australia making up 92% (11/12 mosquitoes) of collections in South Australia (sites 8 and 9) and also appearing sporadically along the east coast of Australia (single individuals identified at sites 15, 16 and 23). The PNG lineages ann-PNG1 and ann-PNG2 accounted for 76% of Cx. annulirostris in PNG (44/ 58 mosquitoes) with the Torres Strait and the top of Queensland's Cape York Peninsula representing their southern limit (sites 23 and 22). A fifth lineage ann-SI occurred only in the Solomon Islands (sites 28 and 29).
Haplotype diversity was very high in all lineages with most lineages showing values above 0.85 (Table 1). Apart from the major lineages described above and the sublineage ann-PNG2, no phylogeographic structure was found among the remaining haplotypes.

Genetic relationships within and between identified COI lineages
To evaluate the effectiveness of the barcoding methodology for identifying species biodiversity, we assessed the inter-and intraspecies divergence before and after the split of Cx. annulirostis and Cx. palpalis into their eight different lineages. For each population (species or lineages) we compared their minimum distance to a congener with the maximum divergence within each population ( Figure 3). A threshold value of 3% was used to separate the graph into four quadrants representing the different categories of species [14,15]. The top right quadrant represents a high intra-and interspecific diversity suggesting that cryptic species are present, and the top left quadrant indicates high interspecific and low intraspecific diversity suggesting no cryptic species. The morphospecies Cx. annulirostris and Cx. palpalis appear in the top right quadrant ( Figure  3A), indicating high levels of genetic diversity within and between species and suggesting these as candidates for a taxonomic split [15]. The presence of Cx. sitiens in the top left quadrant of Figure 3A indicates that it did not display sufficient within-species variation to generate doubt as to whether it was a single biological entity. When the five lineages of Cx. annulirostris and the three lineages of Cx. palpalis, identified through phylogenetic inference, were reanalyzed, all eight lineages appeared in the bottom left quadrant ( Figure 3B), suggesting recently diverged populations and/or newly emerged species [15].

Alternative tree topologies
Maximum Likelihood methods were used to further characterize the phylogenetic relationship by testing alternative (constrained) trees. We used three haplotype subsets and inferred constrained trees using the AU-test and the SH-test [16] to test if the constrained trees were significantly better than our best unconstrained tree ( Figure 4 and Table 2). First we constructed and bootstrapped an unconstrained tree using two alternative heuristic searching algorithms; this found trees showing identical topology with marginal differences in branch support ( Figure  4). The relationship of the three Cx. palpalis lineages was not fully resolved in the unconstrained tree and so we tested whether an alternative branching of these three lineages of Cx. palpalis would be rejected if compared to the unconstrained topology supporting the following: [(pal-S-AUS, pal-PNG), pal-N-AUS]. The AU-test and SH-test could not reject the alternative topologies ( Table 2, Nos. I and II), indicating a trichotomy of the three lineages due to the lack of a robust phylogenetic signal.
Next we tested if we could reject the monophyly of the Australian lineages of Cx. annulirostris ann-AUS and ann-S-AUS as these two lineages appeared to be polyphyletic on the unconstrained tree ( Figure 4). The AU-test and SHtest rejected this constraint in subset 1 and 2 ( Table 2, Nos. III), and thus supported the separate evolutionary origin of the two Australian Cx. annulirostris lineages. In subset 3, this topology was not rejected although the Pvalues for both tests were low. Similarly, the monophyly of the Cx. annulirostris lineage ann-PNG2 with ann-PNG1 in PNG was rejected by both tests in all three subsets ( Table 2, Nos. IV).
Phylogenetic tree of Culex spp. based on COI gene sequence

Culex annulirostris (ann SI)
Culex annulirostris (ann PNG-1) The Cx. annulirostris lineage ann-SI from the Solomon Islands proved problematic as its placement on the phylogenetic tree was ambiguous (Figure 4). Neither the AUtest nor the SH-test could reject the alternative placing of ann-SI: (i) as a sister to the rest of Cx. annulirostris with Cx. palpalis (

Discussion
Culex annulirostris and Cx. palpalis have overlapping morphology and are made up of several distinct COI lineages whose major groupings are congruent with the ITS1 diagnostic developed to separate these cryptic species [12]. Culex sitiens was most divergent and showed little genetic or geographic structure throughout our collection sites in Australia, PNG and Timor Leste. Its use of salt and brackish water larval habitats has allowed for the rapid exploitation of uniform coastal habitats throughout an extensive distribution that spans from Asia to Australia [6,17].
Culex palpalis comprises three geographically structured COI lineages. The branch to the pal-S-AUS lineage from southern Australia (site 10) is well supported. The pal-PNG and pal-N-AUS lineages are supported biologically in that they appear restricted to southwest PNG and the Torres Strait (pal-PNG, sites 23, 24 and 25) and to northern Australia (pal-N-AUS, sites 1, 2, 18, 20 and 22). The larval habitats of this mosquito are fresh-water sites with relatively low levels of organic matter [6].
The four major lineages of Cx. annulirostris indicate extended allopatric isolation, while the sublineage ann-PNG2 is a more recent event. The ann-SI lineage includes specimens from the north and south Solomon Islands and probably represents a separate Pacific island species. The ann-S-AUS lineage is more common throughout southern Australia and is found in much lower relative numbers along eastern Australia and in Torres Strait; no ann-S-AUS individuals were identified from the Northern Territory or Western Australia. The Australian lineage (ann-AUS) is the largest and most widespread, found throughout Australia and extending well into PNG with one haplotype found in Timor Leste (site 30). There is increasing evidence that ann-AUS may not have the intrinsic or extrinsic ability to be an effective JEV vector. Bloodmeal studies from Cx. annulirostris mosquitoes collected in northern Queensland and Cape York, that would represent ann-AUS, indicate a feeding preference for marsupials, thus diverting host-seeking mosquitoes away from pigs and decreasing this lineage's efficiency as JEV vector [18]. Additionally, JEV vector competency studies suggest that ann-AUS may be a relatively inefficient laboratory vector for the JEV genotype I strain which has been present in the Torres Strait and northern Queensland since 2000 (A. F. van den Hurk, unpublished data). The ann-PNG1 and ann-PNG2 lineages exist in PNG and the Torres Strait, and though the monophyly of these two lineages is rejected, they both show a southern limit at the top of Australia's Cape York Peninsula (site 22), which correlates exactly with the current southern limit of JEV activity [5].
In light of this COI diversity it is not surprising that Cx. annulirostris is found in a wide variety of larval habitats including fresh and slightly brackish water, and in habitats with relatively high levels of organic matter as well as transient habitats [6,19,20]. If these divergent lineages represent separate biological species, it is unlikely that morphology will distinguish these taxa and another DNAbased diagnostic tool will be required to study these mosquitoes.

Mosquito phylogeography in Australasia
The geological events of the Miocene, Pliocene and Pleistocene are believed to be responsible for considerable speciation events in this region [21,22]. There were probably two dispersal opportunities for culicid fauna to move east into the Australian region. The first was during the early Pliocene (5-3.4 mya) when the Indo-Malayan Archipelago was in place and an easterly spread of Oriental fauna was possible. The second was during the Pleistocene glaciation periods (1.6-0.01 mya), when vast areas of the     Maximum Likelihood -PhyML / PAUP* A pelagos) and Sahul shelf (joining Australia and New Guinea) were exposed, facilitating the movement of fauna down the Indo-Malayan Archipelago [23]. Present coastlines of New Guinea and northern Australia were formed approximately 15,000-8,000 years ago and the land bridge between Australia, the Torres Strait and New Guinea was last flooded 8,000-6,000 years ago [23,24].
We suggest two different biogeographic histories for these Culex taxa. Culex annulirostris and Cx. palpalis have distributions limited mostly to Australasia, with genetic and geographic structure suggestive of an extended evolutionary history in this region allowing the evolution of multiple divergent lineages. Thus Cx. annulirostris, Cx. palpalis or an ancestor thereof appeared during the early Pliocene (5-3.4 mya), which would have permitted the necessary evolutionary time for geographic expansion and the development of divergent lineages. Since Cx. sitiens displays little genetic or geographic structure in Australia and has a distribution spanning Australasia and Southeast Asia to as far north as India [17], we suggest a more recent expansion into Australasia, probably during one of the more recent Pleistocene glaciations (1.6-0.01 mya).

Barcoding closely related Culex taxa
The mtDNA COI sequence has been assessed as a marker for evaluating mosquito diversity and has proved useful in DNA barcoding studies of mosquitoes across several genera and species identified through conventional morphological taxonomy [25,26]. In insect molecular systematics, other markers have been used with success: 18S rDNA, 28S rDNA, NADH dehydrogenase subunit 5 and cytochrome oxidase II [27,28]. Here we have used the COI marker on closely related Culex mosquito taxa that were genetically identified to species using the ITS1 [12]. We employed a Maximum Likelihood framework for hypothesis testing [16] that provided insights into the evolutionary history of these three taxa. As both ITS1 markers and COI con-curred with the latter, revealing several more divergent lineages within these taxa, we advocate that COI is a reasonable starting point for molecular identification of potential cryptic mosquito species of the genus Culex.

Conclusion
The different geographic distributions of these distinct lineages suggest biological variety and thus it is reasonable to assume that many of these lineages will have different abilities to transmit endemic and exotic arboviruses. The coincidental southern limit of ann-PNG1, ann-PNG2 and JEV activity presents a plausible hypothesis as to why JEV has not established on the Australian mainland, despite the apparent abundance of local Cx. annulirostris vectors and feral pig amplifying hosts [3]. As stressed above, the endemic ann-AUS lineage may not be an effective JEV vector due to its local marsupial feeding preferences and relative inefficiency in transmitting the JEV genotype I strain and thus may provide northern Australia with a natural buffer zone [18]. If either ann-PNG1 or ann-PNG2 is responsible for this JEV activity it is important to determine their species status and monitor their distributions to determine if they are moving south into Australia. If these lineages are not separate species then there is the possibility for gene flow from the PNG lineages to the ann-AUS lineage on the Australian mainland, and this may enhance the JEV potential of local ann-AUS populations. Analysis of the vector competency of individual lineages is now required to characterize their intrinsic ability to transmit JEV, while nuclear DNA studies on sympatric populations would establish if natural mating barriers exist.
The question must now be asked as to whether ann-PNG1 and ann-PNG2 are exotic taxa naturally expanding their range from southwest PNG into Australia -or are we observing the effects of climate change, such as have been suggested for the spread of the bluetounge arbovirus  through Europe alongside the northward movement of its Culicoides vectors [29]. In Australia, rapid shifts of latitude clines in Drosophila over the last 20 years have provided evidence for biological changes through regional warming in Queensland [30], and this may also facilitate the expansion of independently mobile fauna from New Guinea.

Specimen collection and identification
Mosquitoes were collected from 43 sites representing 30 map locations in Australia, PNG, Timor Leste and the Solomon Islands (Bougainville and Guadalcanal) (see Figure 1, see Additional file 1 and 2). Adult mosquitoes were collected using CO 2 -baited encephalitis virus surveillance (EVS) traps with and without 1-octen-3-ol (octenol). Specimens were morphologically identified using the keys of Lee et al. [6] and Marks [31]. Mosquitoes were stored in liquid nitrogen, dry ice, on silica gel, or in 70% ethanol prior to total DNA extraction. Colony Cx. annulirostris from the Army Malaria Institute (Brisbane, Queensland, Australia) were used as reference material. Total DNA was extracted from mosquitoes using a salt extraction and ethanol precipitation procedure [12]. Due to problems with adult morphology, all material was genetically identified to species by an ITS1 PCR-RFLP procedure previously developed to discriminate between Cx. annulirostris, Cx. palpalis and Cx. sitiens [12].

Genetic analysis COI amplification
A 538 bp 5' fragment of the COI gene was PCR amplified and sequenced using the same primer pair for amplification and sequencing; F-COI50 (5'-GTA GTT TAG TAG AAA ATG GAG C-3') and R-COI650 (5'-TAG CAG AAG TAA AAT AAG CTC G-3'

COI sequence analysis
Individual sequences were assembled with Sequencer 4.2.2 (GeneCodes, MI, USA). Nucleotide and haplotype diversity within the lineages identified was calculated using DNASP 4.10 [32]. Identical haplotypes were pooled and only unique haplotypes were used for further analysis. Composition of the nucleotide sequences was analyzed using MEGA 3.1 [33]. Sequence divergences were calculated using the Kimura 2 parameter distance model using MEGA 3.1 [33]. The maximum of intra-population distance and the minimum of inter-population distance were calculated using MEGA 3.1. We applied a 3% threshold to represent different categories of "species" [14].  [34]. The robustness of the Maximum Likelihood tree was evaluated by the bootstrapping method with 500 replicates using PhyML. For the nucleotide model selection we employed a hierarchical likelihood ratio test (LRT) as well as the Akaike information criterion (AIC) implemented in ModelTest 3.6 [13] in cooperation with PAUP* 4b10 [35].
In addition, the dataset was analysed by Bayesian phylogenetic analysis using MrBayes 3.1.2 [36]. We took advantage of MrBayes' ability to relax the parameters of the nucleotide model over subsets of the alignment, in order to better model the nucleotide evolution -particularly at different nucleotide coding positions [36]. A covarion model was used to better model the between-lineage variability [37].
Initially the alignment was divided into partitions based on coding position. Then we unlinked the parameters (shape, revmat, statefreq) between these partitions and applied a 4× 4 nucleotide model. Finally, for the 1st and 2nd codon positions we used the model with only one substitution category with all rates equal (F81 model), and for the 3rd codon position we used the model with 6 categories with a gamma shape parameter plus invariants including the covarion parameter (GTR+Γ+I+cov model).
Metropolis-coupled Markov chain Monte Carlo analyses were run with one cold and three heated chains (temperature set to default 0.2) for 5,000,000 generations and sampled every 200 generations. This process was performed three times from a random starting tree and ran well beyond convergence. Trees before convergence were discarded for the reconstruction of the consensus Bayesian tree with posterior probabilities.
The best trees and all constraints were inferred in PAUP*4b10 [35]. We first reconstructed a Neighbour joining tree and used it to estimate the GTR+Γ+I likelihood parameter. Then the parameters were fixed and used in the inference of a Maximum Likelihood tree using a heuristic search with 20 random sequence additions with NNI swapping. The resulting GTR+Γ+I model parameters were used for the Maximum Likelihood tree reconstruction for the unconstrained tree as well as for all constrained trees. For the unconstrained trees we calculated bootstraps using 100 replicates. Site likelihoods for individual trees were calculated using PAUP*4b10 [35] and these were used for the Approximately Unbiased (AU) test [16] and the Shimodaira-Hasegawa (SH) test [38], both implemented in CONSEL 0.1 h [39]. A value of P>0.05 was considered statistically significant to reject the hypothesis that the two trees were significantly different.