The species flocks of cichlid fishes in the East African Lakes Tanganyika, Malawi and Victoria are prime examples of adaptive radiation and explosive speciation. Several hundreds of endemic species have evolved in each of the lakes over the past several thousands to a few millions years. Sexual selection via colour-assortative mating has often been proposed as a probable causal factor for initiating and maintaining reproductive isolation. Here, we report the consequences of human-mediated admixis among differentially coloured populations of the endemic cichlid fish Tropheus moorii from several localities that have accidentally been put in sympatry in a small harbour bay in the very south of Lake Tanganyika. We analysed the phenotypes (coloration) and genotypes (mitochondrial control region and five microsatellite loci) of almost 500 individuals, sampled over 3 consecutive years. Maximum-likelihood-based parenthood analyses and Bayesian inference of population structure revealed that significantly more juveniles are the product of within-colour-morph matings than could be expected under the assumption of random mating. Our results clearly indicate a marked degree of assortative mating with respect to the different colour morphs. Therefore, we postulate that sexual selection based on social interactions and female mate choice has played an important role in the formation and maintenance of the different colour morphs in Tropheus, and is probably common in other maternally mouthbrooding cichlids as well.
The adaptive radiations of cichlid fishes in the East African Great Lakes Tanganyika, Victoria and Malawi remain the most astounding examples of morphologically, behaviourally and ecologically diverse species flocks (Fryer & Iles 1972; Stiassny & Meyer 1999). The intriguing diversity and species richness of the cichlid assemblages of these lakes, each of which comprises hundreds of endemic species that have evolved in the last several thousands to a few million years, established them as a prime model system for the study of evolution (Fryer & Iles 1972; Meyer et al. 1990; Stiassny & Meyer 1999; Kornfield & Smith 2000; Verheyen et al. 2003; Kocher 2004; Salzburger & Meyer 2004).
Adaptive radiation requires external physical events that provide the appropriate environment and, in many cases, intrinsic biological factors (‘key innovations’) that give particular lineages the potential to radiate (Simpson 1953; Schluter 2000). With regard to East African cichlids, the evolutionary success has been attributed to the interaction of different types of biological factors as well as the geological and climatological framework in which cichlid evolution has taken place (e.g. Sturmbauer 1998; Kornfield & Smith 2000). One hypothesis to explain the species richness of cichlids refers to the evolutionary significance of the adaptable pharyngeal jaw apparatus (Liem 1973). More recent studies have put forward the hypothesis that sexual selection through female choice of male (nuptial) coloration might have played an important role in the evolution of East African cichlids (Dominey 1984; Turner & Burrows 1995; Deutsch 1997; Seehausen & van Alphen 1999; Danley & Kocher 2001; Knight & Turner 2004). Speciation by disruptive sexual selection in cichlids has been proposed on the basis of field observations (van Oppen et al. 1998) as well as mate choice experiments in the laboratory (Knight et al. 1998; Seehausen et al. 1999; Knight & Turner 2004). Further evidence for sexual selection as an important isolating mechanism comes from the observable breakdown of visual reproductive barriers under monochromatic light conditions or under turbid waters resulting from human inference (Seehausen et al. 1997). The occurrence of assortative mating in natural cichlid populations has so far not been surveyed at a larger scale using population genetic methods.
Here, we report on a human-mediated admixis of differentially coloured Tropheus moorii populations that were put in sympatry in a small bay in the very south of Lake Tanganyika. The genus Tropheus is in need of taxonomic revision (Snoeks et al. 1994). More than 100 differentially coloured morphs can be distinguished in T. moorii, with almost every continuous stretch of rocky shoreline of Lake Tanganyika being inhabited by its own local colour morph (Sturmbauer & Meyer 1992; Baric et al. 2003; Schupke 2003; Sturmbauer et al. 2005). Both males and females typically display the same coloration, while juveniles show a more cryptic, often striped, phenotype. Despite marked differences in coloration and, often, considerable genetic distances between populations (Sturmbauer & Meyer 1992; Baric et al. 2003; Sturmbauer et al. 2005), T. moorii occupy the same ecological niche all around Lake Tanganyika. Also, their overall morphology (except coloration) is highly similar, and no differences in breeding behaviour and spawning time have been observed in T. moorii (Sturmbauer & Meyer 1992; Baric et al. 2003; Schupke 2003). Therefore, it has been argued that in T. moorii ecology and morphology are under stabilizing selection, while coloration appears to be a sexually selected trait driving allopatric speciation under morphological stasis (Sturmbauer & Meyer 1992).
In June 1998, local fishermen collected about 300 adult individuals of T. moorii from several sites in the southern part of the lake, with the intention of exporting these colourful fishes for the aquarium trade. Owing to the fact that the fishing was carried out without concession, Zambian authorities refused export permits. Instead of returning the fishes to their original habitats, as instructed by the local authorities, the catch was released in a small harbour basin of not more than 200 m2 in size in front of the Fisheries Department in Mpulungu, Zambia (L. Mwape 1999, personal communication).
This artificial amalgamation of several differently coloured populations of T. moorii (figure 1) provided the unique opportunity to study the biological interactions between several colour morphs of the same cichlid species in their natural environment. It also resembles a situation as it may have existed during previously reported major low water levels of Lake Tanganyika, which led to the admixis of several formerly isolated populations (Sturmbauer 1998; Kornfield & Smith 2000; Sturmbauer et al. 2001). We analysed DNA sequences of the first section of the mitochondrial control region (442 bp) as well as five microsatellite loci from 457 specimens sampled consecutively over a period of three years from the Mpulungu harbour bay. We tested whether or not members of the same colour morph mate assortatively and to what extent hybridization had occurred between different colour morphs in the admixed population, applying both maximum-likelihood-based parenthood analyses (Marshall et al. 1998; Slate et al. 2000) and Bayesian inference of population structure (Pritchard et al. 2000).
2. Material and methods
Sampling was carried out in February 1999, 2000 and 2001, which corresponds to 0.5, 1.5 and 2.5 years after the release of non-indigenous specimens in the harbour bay of Mpulungu, Zambia. Fishes were collected with gill nets, weighed, sized, sexed and photographed (table 1). Finally, a piece of the caudal fin was taken for DNA extraction and preserved in 100% ethanol before the individuals were released. An adjacent population, situated about 50 m away from the admixed population, was sampled as reference group, leading to a total of 457 specimens (see table S1, in the electronic supplementary material).
(b) Morphological data
A principal component analysis (PCA) was carried out among individuals whose total length (TL) was more than 60 mm (n=360), since juveniles of T. moorii of less than about 60 mm in length display an almost indistinguishable stripe pattern. For the reference population, only adult individuals of the first year of sampling were included in this analysis. Twelve features related to coloration were used for this analysis (see figure 2a): overall body colour (red/light(=light olive)/dark(=dark olive)/orange), central body colour (red/yellow/dark/orange), colour of eyelid (red/light/dark/yellow), eye-ring (blue/dark/light), operculum (red/dark/light/blue), operculum edge (red/light/dark/yellow/orange/blue), dorsal fin (dark-red/light/dark/light-blue/light-red), base of dorsal fin (dark-red/light/dark/orange/blue/light-red), base of anal fin (dark-red/light/dark/orange/blue/light-red), base of pectoral fin (dark-red/light/dark/orange/blue/light-red), stripe/dot pattern (uniform/stripe/dot) and dorsal fin pattern (uniform/striped). Characters were translated into a binary data matrix and analysed in a PCA.
(c) Molecular methods
Total DNA was extracted from fin-clips preserved in 100% ethanol applying a proteinase K digestion followed by sodium chloride extraction and ethanol precipitation (Bruford et al. 1998). PCR amplification was performed according to standard methods on an ABI 9700 thermocycler (Applied Biosystems) for the mitochondrial DNA, and on an air thermocycler (Idaho Technologies) for the microsatellite loci. We used published primers for both the amplification of a 442 bp segment of the mitochondrial control region (Kocher et al. 1989; Salzburger et al. 2002), as well as for the five microsatellite loci Pzeb3, TmoM11, TmoM25, ULI2 and UME002 (forward primers were labelled with fluorescent dyes FAM or HEX; Parker & Kornfield 1996; Zardoya et al. 1996; van Oppen et al. 1997). The PCR fragments of the control region were purified using the ExoSAPIT enzyme mix (USB), directly sequenced with the BigDye sequencing chemistry (Applied Biosystems), and analysed on an ABI3700 automatic sequencer (Applied Biosystems). The microsatellite loci were analysed on the same device using the internal size marker Genescan 500 (Applied Biosystem).
(d) Data analyses
DNA sequences were aligned using Sequencher 4.0 (Genecodes) and genetically characterized based on a large body of published data from T. moorii (Sturmbauer & Meyer 1992; Baric et al. 2003; Sturmbauer et al. 2005). A haplotype network was constructed with the computer program TCS (Clement et al. 2000). In the case of alternative branching orders, those ones were chosen that were indicated by a maximum-likelihood analysis in PAUP*4.0b10 (Swofford 2002), after translating the maximum-likelihood tree into an unrooted network. We then mapped the colour information of all mitochondrial haplotypes, for which colour data were available, onto the haplotype network.
For the microsatellite data, we estimated allele frequencies for every locus using Arlequin 2.1 (Schneider et al. 1999). Departure from Hardy–Weinberg expectations for every locus was tested within the different partitions of our dataset using a test analogous to Fisher's exact test (Guo & Thompson 1992), as implemented in Arlequin. Linkage disequilibrium for all pairs of loci was tested for the same partitions with Arlequin. Genetic differentiation between the four groups, ‘light-olive’, ‘dark-olive’, ‘red’ and ‘striped-red’, was measured with Wright's F-statistics (FST; Weir & Cockerham 1984) as implemented in Arlequin (because of its rare occurrence, ‘orange’ was not included). This analysis was performed with both microsatellite and mitochondrial control region data. Critical significance levels for multiple testing were corrected following the sequential Bonferroni procedure (Rice 1989).
Parenthood tests were carried out for all specimens that were born after admixis of the differentially coloured populations. The classification of these individuals was based on growth rates for exactly this population (Egger et al. 2004). These growth rates of T. moorii were delineated from a mark–recapture study in the Mpulungu harbour using chemical tagging of otoliths to examine increment formation. Accordingly, for the 1999 sample, individuals of less than 65 mm TL were considered as juveniles conceived after secondary admixis; for the 2000 sample, individuals of less than 78 mm TL were included; and for the 2001 sample, individuals of less than 82 mm TL were defined as juveniles born in the admixed population. Maximum-likelihood-based parenthood tests were initially performed using the computer program Cervus 2.0 (Marshall et al. 1998; Slate et al. 2000), with all individuals being considered as potential parents. The probabilistic parent–offspring relationships proposed by Cervus were further evaluated by computing likelihood ratios for short tandem repeats (STRs) (see Hammnond et al. 1994). The additional information provided by the mitochondrial DNA sequences was accounted for using Bayes' theorem. To distinguish between real candidate parents and siblings that also could be identified as most likely parent(s), we used the information on sampling date and total length of each individual to discern parentage.
As a complementary approach to the morphological evaluation of recognized parent–offspring pairs, which excludes all individuals that either lack colour information or that have unknown parents, we performed a population assignment test. To this end, we used a Bayesian clustering method implemented in Structure 2.1 (Pritchard et al. 2000) using the microsatellite data and coding the mitochondrial haplotypes as a sixth marker. Here, our strategy was not to infer the population structure and the number of distinct clusters (K) from the genetic data available (default mode in Structure). Instead, we used the information provided by the morphological evaluation of the adult specimens based on their coloration as a prior in the ‘learning phase’ (burn in), in order to test the genetic assignment of the offspring individuals. This has been shown to be an accurate tool to detect immigrants (e.g. Pritchard et al. 2000) and/or to identify hybrid individuals (e.g. Beaumont et al. 2001). We ran Markov chain Monte Carlo simulations with 500 000 replications (burn in=50 000; admixture model with prior population information; correlated allele frequencies; PCA results as prior population information) for K (number of genetic clusters)=5 (based on the five phenotype groups ‘light-olive’, ‘dark-olive’, ‘orange’, ‘red’ and ‘striped-red’).
We then used the results from the parenthood tests and from the genetic assignment to calculate the ratio of intra-morph mating events versus inter-morph matings, and compared this ratio to the expected ratio under the assumption of random mating using a chi-square goodness-of-fit test.
PCA demonstrated the existence of five groups of distinctly coloured individuals in the admixed population (‘light-olive’, ‘dark-olive’, ‘orange’, ‘red’ and ‘striped-red’ in figure 2a). Typically, for the analysis of presence/absence data, a large number of principal components are needed to account for most of the variation (Manly 1994). In this case, however, the main groupings showing the variability we were interested in were evident in the first two axes. All adult fishes from the reference population sampled in the first year after admixis were grouped within the ‘light-olive’ phenotype confirming this phenotype as the indigenous one. These fishes resemble the ‘Mbita’ type, named after the locality from where these fishes were initially exported for the aquarium trade. Although data on the exact sampling localities for the introduced specimens were not available, most of the fishes could be assigned to populations from a specific stretch of shoreline based on their characteristic colorational morphotype and their mitochondrial haplotype (Sturmbauer & Meyer 1992; Baric et al. 2003; Schupke 2003; Sturmbauer et al. 2005; see figure 1). Based on their coloration, the dark-olive individuals are likely to have originated from populations on the Zambian east coast of Lake Tanganyika (morphologically resembling individuals that are found between Kala and Chituta Bay). Likewise, the orange (‘Ilangi’ type), red (‘Chilanga’ type) and striped-red (‘Chimba’ type) individuals were assigned to the shoreline northwest of the Lufubu estuary, between Cape Inangu and Moliro.
A total of 56 mitochondrial haplotypes was observed, of which 19 were clearly distinct and occurred exclusively in the orange, red and striped-red individuals (figure 2b). Seven out of the 21 haplotypes of the reference group were not present in the admixed population. Mitochondrially, all light- and dark-olive individuals including the reference population were grouped with DNA sequences previously assigned to lineage A2 according to Baric et al. (2003; equivalent to TCS-1 in Sturmbauer et al. 2005). The individuals with orange or red phenotypes, and all but one striped-red fish clustered within lineage F (Baric et al. 2003; TCS-7 in Sturmbauer et al. 2005). This single striped-red individual, resolved within lineage G (Baric et al. 2003; TCS-8 in Sturmbauer et al. 2005), most likely stems from the population at Katoto, which was previously characterized as heterogeneous due to admixis, comprising intermediate phenotypic traits and three mitochondrial haplotype lineages (A2, A4 and G; Baric et al. 2003; Sturmbauer et al. 2005).
F-statistics based on the mitochondrial DNA sequences and microsatellite data revealed no significant population differentiation between the groups of light- and dark-olive phenotype (table 2), which might be due to the origin of several individuals from populations such as Katoto that contain individuals assigned to both colour groups. Although distinct in coloration, the groups of red and striped-red individuals were not genetically differentiated from each other. All remaining pairwise FST comparisons revealed significant population differentiation. The individuals of the adjacent reference population showed, based on the microsatellites, no significant population differentiation from the light-olive phenotypes (the indigenous group of the harbour bay), while they were distinct from all other groups (table 2).
Based on the microsatellite data, no linkage disequilibrium was found in the dark-olive fish and the reference population. In the light-olive individuals, 4 out of 20 pairwise comparisons indicated linkage disequilibrium, which is most likely due to the fact that at least one introduced population plus the indigenous fishes were grouped into this cluster. Two loci each were found to be linked to the red (ULI2 and UME002) and striped-red (TmoM11 and UME002) individuals. However, both groups contained a relatively small number of individuals. Also, it is not known whether all red and striped-red fish originated from only one original population each. In the juvenile individuals sired after admixis, 14 out of 20 pairwise comparisons were indicative of a linkage disequilibrium. Similarly, three loci showed a significant heterozygote deficit in the juvenile individuals, while in the dark-olive, red and striped-red fish no deviation from Hardy–Weinberg equilibrium was found. In the light-red and the reference population, a heterozygote deficit was found in one locus (TmoM25).
The parenthood tests targeting the individuals sired after the secondary admixis using all specimens of the admixed population as candidate parents identified parents for 52 individuals. For 41 individuals one, and for 11 individuals both, parents were determined. Forty-one (78.9%) of these offspring individuals displayed the same phenotype as their parents. However, three light-olive individuals were assigned to a dark-olive parent (5.7%), and seven dark-olive individuals (13.5%) were likely to have a light-olive parent indicating several mating events between these two groups. One red offspring individual (1.9%) was likely to have had an orange mother.
The microsatellite-based Bayesian inference of population structure (Pritchard et al. 2000) provided a more detailed picture of the genetic composition of the admixed population's individuals (figure 3). The light-olive phenotypes of the admixed assemblage were grouped into one genetic cluster (class A genotypes; figure 3a). Likewise, the dark-olive individuals were clustered together (class B genotypes; figure 3b). All red, orange and striped-red phenotypes were genetically resolved into a single group (class C genotypes; figure 3c–e). A fourth class of genotypes was found primarily in the reference population (class D genotypes; figure 3f), a fifth group was determined based on genetic grounds but was not recognized morphologically. These class E genotypes (yellow bars in figure 3) could possibly represent a cryptic population among light-olive phenotypes from an originally isolated spot that was released with all the other non-indigenous individuals. As additional information about class E genotypes was not available, these were excluded from further analyses.
About 63% (114 out of 180) of the offspring in the admixed population (figure 3g) were assigned to a particular genotype class with a probability Pa of more than 0.75, which we considered as juveniles of intra-genotypic matings. The value for Pa>0.75 seems rather high, given the expected probability of about 0.5 for an (F1-) hybrid individual. However, we chose the value Pa>0.75 for intra-genotypic matings based on the observation that, in our case, with this threshold an alternative (hybrid) origin of a tested juvenile could be ruled out in more than 90% of the cases (based on the upper bound of the probability interval). In addition to these 63% of the offspring, 5% of the offspring individuals (9 out of 180) were assigned to matings between class A and class D genotypes (reference group), which show the same coloration (light-olive), and, thus, were also considered as offspring from intra-morph matings. Accordingly, 68.3% (123 out of 180) of offspring originated from within morph matings. This is significantly more than could be expected under the assumption of random mating (; p<0.01). Only three individuals (1.6%) originated from matings between ‘olive’ and ‘reddish’ parents, which is equivalent with matings between different mitochondrial haplotype groups. This number is significantly smaller than could be expected under random conditions (; p<0.01).
Cichlid fishes are prime examples where ‘selective mating’ (Kosswig 1947) is believed to have played an important role in speciation processes. In the Central American midas cichlid (Amphilophus citrinellus), for example, assortative mating has been demonstrated by means of laboratory experiments and field observations (McKaye & Barlow 1976; Barlow 1977; Barlow & Rogers 1978), and it has been argued that this form of sexual selection is the main force maintaining the colour polymorphism of a cryptic, striped ‘normal’ and a conspicuous ‘golden’ morph (McKaye 1980; Barlow 1983, 2000). Similarly, disruptive sexual selection via colour-assortative mating has been suggested as an important factor that is at least partially responsible for the evolution of the myriad of cichlid species in the East African Great Lakes (e.g. Dominey 1984; McKaye 1991; Danley & Kocher 2001; Allender et al. 2003). More than 100 different colour morphs of T. moorii are among the most famous examples, where sexual selection on colour traits is likely to have triggered diversification (Sturmbauer & Meyer 1992; Sturmbauer 1998; Schupke 2003). Still, T. moorii is somewhat outstanding among the haplochromine cichlids that include the Tropheini (e.g. Salzburger et al. 2002, 2005), in that it does not show sex-based colour polymorphism. Tropheus moorii displays a complex mating system, in which colour is not only likely to be involved in sexual selection, but also in the context of intraspecific social interactions—regardless of sex (Sturmbauer & Meyer 1992; Sturmbauer & Dallinger 1995; Sturmbauer 1998; Schupke 2003). Thus, assortative mating based on coloration is likely to act similarly to that found in the haplochromine cichlids from Lakes Victoria and Malawi providing the basis of population differentiation and speciation (e.g. Dominey 1984; Turner & Burrows 1995; Deutsch 1997; Seehausen & van Alphen 1999; Danley & Kocher 2001; Knight & Turner 2004; Kocher 2004), with the additional feature of being critical for social interactions within populations. The lack of sexual colour dichromatism in Tropheus is explained by the importance of sex-independent social signals.
The parenthood analyses for the offspring of the admixed T. moorii populations revealed that about 80% of the positively typed individuals had the same phenotype as their probable parent(s), suggesting a marked degree of assortative mating with respect to the different colour morphs. This ratio of within-population fertilization is higher than the one observed in laboratory trials with five populations of Pseudotropheus zebra from Lake Malawi (Knight & Turner 2004). However, in more than half of the cases our sampling in the Mpulungu harbour bay recovered only one parent, so that the possibility remains that the second (unknown) parent might belong to a different colour morph.
Our second approach, the population assignment test, overcomes the problem of unknown parent or offspring phenotypes, as it clusters individuals according to their genotypes only. Given that the recovered genotype classes are in agreement with phenotypic clusters, offspring of within-colour-morph matings should have a high probability of being assigned to only one genotype class (the one to which both parents belong), while the genome of hybrids between colour morphs should carry portions of both parental genotype classes. In our case, the population assignment tests (Pritchard et al. 2000) recovered the adult individuals with light- and dark-olive phenotypes as well as the reference group (light-olive phenotype) as distinct genotype classes. The red, orange and striped-red individuals were, however, grouped into a single genotype class (figure 3). Based on these assignments, about 68% of the offspring of the admixed individuals are likely to be derived from within-colour-morph matings (Pa>0.75), which is significantly more than could be expected under random mating (p<0.01). This value is similar to the frequency of within-population matings found in laboratory trials with P. zebra from Lake Malawi (Knight & Turner 2004).
Most inter-genotypic matings occurred between individuals assigned to class A and class B genotypes, which correspond to light- and dark-olive phenotypes, respectively. This is also reflected in the low FST-value when comparing these two clusters. In their experiments with P. zebra, Knight & Turner (2004) observed that two populations, which were not the most closely related ones, did not mate assortatively, and they interpreted this as due to the relative morphological resemblance of these populations with respect to each other. In our natural set-up, the light- and dark-olive phenotypes differ primarily in the main body coloration and both groups show a more or less pronounced yellow blotch on their flanks (figures 1 and 2). They also fall into the same mitochondrial haplotype cluster (figure 2), which implies that they are, in fact, more closely related compared to the reddish ones. The parenthood analyses also recovered one mating event between red and orange fish. This is not surprising based on their genetic similarity and the morphological resemblance with red coloration. Since their genotypes were clustered—together with the striped-red fish—into one genetic cluster (class C genotypes), no further evaluation of matings between these three phenotype groups was possible. The most striking result was that only three out of all 180 juveniles were found to be ‘hybrids’ between ‘olive’ and ‘reddish’ parents and, hence, between two different mitochondrial haplotype lineages, pointing to a marked degree of assortative mating. The occurrence of assortative mating is further supported by the observed deviation from Hardy–Weinberg equilibrium as well as the linkage disequilibrium in the juvenile individuals that were sired after admixis.
In spite of the philopatric behaviour of Tropheus, the genetic consequences of the human-induced secondary admixis were not restricted to the harbour bay, where the fishes had been released. The reference population, which is situated about 50 m away from the location of admixis, turned out to be greatly affected as well. While in the first year of sampling the specimens of the reference population consisted exclusively of class D genotypes (white bars in figure 3f), the frequency of these indigenous genotypes decreased over the sampling period so that in the third year of sampling more than 80% of the reference population consisted of introgressed genotypes or hybrids between introgressed and indigenous fishes (figure 3f). A morphological evaluation of these introgressants or hybrids was not possible, since a large number of the non-indigenous genotypes belong to class A corresponding to the light-olive phenotypes, which are morphologically indistinguishable from the reference population's fish. Also, many individuals collected there in 2000 and 2001 were smaller than 60 mm and, therefore, not suitable for morphological analyses.
That migration between adjacent populations occurs naturally can be detected based on the low FST-values between the reference population's individuals and the light-olive individuals (table 1) as well as in one individual in the light-olive phenotypes of the admixed population that genetically belongs to the reference group (marked by an asterisk in figure 3a), and thus most likely represents an immigrant from the reference group before admixis. However, natural migration seems to have occurred at rather low frequencies compared to the rapid dispersal of introduced genotypes into the reference population after admixis. The high density of individuals that must have persisted in the small harbour bay after the introduction of 300 individuals might be the driving force for migration of introduced individuals into adjacent rocky habitats.
Our approach combining parenthood analyses, population pairwise FST-values and population assignment tests revealed that complex interactions take place between allopatric colour morphs of T. moorii when put in sympatry in their natural environment. For the first time, our study shows that colour morphs of T. moorii, which do not have any contact in nature, mate assortatively in the presence of other colour morphs. Assortative mating appears to be even stronger between the two morphologically and genetically redefined clusters ‘olive’ and ‘reddish’. Assortative mating, i.e. the observation that individuals of two or more classes tend to breed with their own kind, may be based on different features in fishes. In the case of the generally colourful cichlid fishes (coloration is why they are called Buntbarsche in German), body coloration is generally accepted to be the decisive feature of mate choice (McKaye 1980, 1991; Barlow 1983, 2000; Dominey 1984; Turner & Burrows 1995; Danley & Kocher 2001; Allender et al. 2003)—at least in maternal mouthbrooders. Other examples for assortative mating in fishes involve exaggerated male traits such as the elongated caudal fins of male swordtails of the genus Xiphophorus that are selected for through female choice (Ryan & Wagner 1987; Basolo 1990, 1995), chemical (olfactory) cues (e.g. McLennan & Ryan 1999), differences in spawning time and/or locality (e.g. Hendry et al. 2004; Østbye et al. 2004; Fraser & Bernatchez 2005; Hendry & Day 2005; McLean et al. 2005), or size (e.g. McLean et al. 2005). Given that there are no detectable differences in overall morphology, ecology, spawning behaviour and timing in T. moorii, and since local differences in natural selection are improbable, we consider colour-assortative mating based on female preferences as the most likely explanation for our finding of a marked degree of colour-assortative mating in T. moorii. Also, it seems unlikely that post-zygotic mechanisms (such as reinforcement) account for our observation, since all the many crossings between different colour morphs of Tropheus reported so far produced fully viable hybrid offspring, and clutch sizes were not smaller (e.g. Schupke 2003). Still, the possibility remains that chemical or acoustic cues, for which we did not test, play a role in social interactions in T. moorii. Future studies should also address the question of whether or not genetic drift was associated with the evolution of different colour patterns and divergent female preferences in cichlid populations by breaking up the linkage equilibrium between loci involved in colour patterning and female preference.
Taken together, our results support the hypothesis that colour-assortative mating played an important role in the formation and, later, in the maintenance of the different colour morphs as well as the major genetic lineages in Tropheus (Sturmbauer & Meyer 1992). The data also imply that the degree of reproductive isolation could be a function of time since divergence, since almost all (more than 95%) mating events involving two different colour morphs happened within and not between the mitochondrial haplotype groups (as defined in Baric et al. 2003; Sturmbauer et al. 2005). This indicates that assortative mating might have evolved gradually in the allopatric populations of T. moorii. Thus, (colour-) assortative mating may not only be a causal factor driving sympatric speciation—as proposed for the cichlid species flocks in Lakes Victoria and Malawi (e.g. Turner & Burrows 1995; Kornfield & Smith 2000; Danley & Kocher 2001)—but may as well happen after secondary admixis, whenever colour differences evolved in allopatry before. In this way, sexual selection drives colour divergence in allopatry, to lead gradually to speciation whenever the differences become large enough to influence mate choice (Greenwood 1965; Coyne & Orr 2004; Knight & Turner 2004). It is interesting to note that several authors have argued that sympatric speciation by sexual selection alone is rather unlikely (e.g. Arnegard & Kondrashov 2004; Coyne & Orr 2004). Further experiments, including laboratory mating trials, are currently underway to detail our understanding of assortative mating in the cichlid genus Tropheus.
We would like to dedicate this work to the late Leonard Mwape. We are grateful to our helpers in the field S. Baric, B. Egger, R. Hanel, B. Kirchberger, S. Koblmüller, L. Makasa, G. Musuluta, M. Nabuyanda, C. Rhomberg, R. Shapola; the divers T. Chempatika, A. and L. Musonda, E. Shichizima, W. Simanwe, P. Simuteonde, J. Simuyemba, K. Sudi; and the staff at the Mpulungu Station, Department of Fisheries, Ministry of Agriculture and Cooperatives, Republic of Zambia. We are further grateful to P. Bunje, M. Barluenga, A. Meyer, K. Sefc, two anonymous reviewers and the Editorial Board Member for valuable comments on the manuscript. This research was conducted in the framework of the Agreement of Understanding between the University of Zambia at Lusaka, the Department of Fisheries, Ministry of Agriculture and Cooperatives, Zambia, and the University of Innsbruck (Austria), the University of Berne (Switzerland) and the University of Graz (Austria). Funding was received from the Austrian Science Foundation (project 12339 and 15239-GEN). W.S. was supported by a DOC fellowship of the Austrian Academy of Sciences and a Marie-Curie fellowship of the EU.