Literature DB >> 24260688

Comparative cytogenetics of two endangered leuciscine fish, Squalius aradensis and S. torgalensis (Teleostei, Cyprinidae), from the Iberian Peninsula.

Catarina Nabais1, Massimiliano Rampin, Maria João Collares-Pereira.   

Abstract

In this study, the description of the karyotypes of the endangered chubs Squalius aradensis (Coelho, Bogutskaya, Rodrigues and Collares-Pereira, 1998) and Squalius torgalensis (Coelho, Bogutskaya, Rodrigues and Collares-Pereira, 1998) is presented by means of conventional (Giemsa-staining, Chromomycin A3 (CMA3)-fluorescence, Silver-impregnation (Ag-NORs)) and molecular (fluorescence in situ hybridization (FISH) with 18S rDNA probe) protocols. These endemic sister-species have an allopatric but adjacent distribution in the most southwestern part of the Iberian Peninsula. Diploid chromosome number was invariably 2n = 50 and karyotypes of both species were grossly similar, composed of metacentric and submetacentric elements with a reduced number of acrocentric pairs. Sequential staining using FISH with an 18S rDNA probe, CMA3 and Ag-NORs treatments revealed consistent positive signals located at the end of the short arms of a submetacentric chromosome pair, likely homologous in both species. While providing useful cytogenetic comparative data against other members of the genus Squalius Bonaparte, 1837, the work aimed to draw attention towards the conservation of two narrow-range and highly confined fish species.

Entities:  

Keywords:  Cytotaxonomy; FISH with rDNA; Leuciscinae; NOR-phenotype; chromomycin A3; silver staining

Year:  2013        PMID: 24260688      PMCID: PMC3833748          DOI: 10.3897/CompCytogen.v7i1.4672

Source DB:  PubMed          Journal:  Comp Cytogenet        ISSN: 1993-0771            Impact factor:   1.800


Introduction

The genus Bonaparte, 1837 belongs to the subfamily Leuciscinae, the major element of the Iberian cyprinid fauna. In Portuguese inland waters, four bisexual species with an allopatric distribution (Leunda et al. 2009) are recognized: (Günther, 1868), in most drainages from the Tejo River basin southwards; (Doadrio, 1988), from the most northern smaller drainages of the Atlantic slope to the Mondego River basin; (Coelho, Bogutskaya, Rodrigues and Collares-Pereira, 1998), in the Seixe, Aljezur, Alvor, Arade and Quarteira River basins; and (Coelho, Bogutskaya, Rodrigues and Collares-Pereira, 1998), only present in the southern Mira River basin. Most chubs of the genus were formerly included in the genus Cuvier, 1816 (see Sanjur et al. 2003). The two species with a wider geographic distribution, and (also present in Spain), were the first to be recognized as different taxonomic units. However, some genetic studies (Coelho et al. 1995, Brito et al. 1997) hypothesized the existence of a more complex differentiation pattern in the most south-western Iberian populations. Two new species, with a restricted geographic range, were then described by Coelho et al. (1998), and ,mainly based on meristic, morphometric and osteological traits. Further studies using in-depth mitochondrial and nuclear markers have confirmed that and are separated, but sister-taxa (see Doadrio and Carmona 2003, Sanjur et al. 2003, Mesquita et al. 2005, 2007, Almada and Sousa-Santos 2010, Perea et al. 2010, Waap et al. 2011). Some cytogenetic data were recorded for populations from Arade, Aljezur and Bordeira drainages (currently assigned to ) and Mira (currently assigned to ) (Collares Pereira et al. 1998), but previously to the acknowledgement that they should be considered distinct taxa from (Coelho et al. 1998). Besides, Collares-Pereira et al. (1998) reported higher karyotype variability in chubs belonging to southern populations, when compared to the northern drainages. Therefore, the present work aimed to describe the karyotypes of and using specimens recently collected. Conventional (Giemsa staining, GC-specific CMA3 fluorescence and Ag impregnation) and molecular (rDNA major complex by FISH) cytogenetic techniques were used to characterize both species chromosome sets. Both endemics are “Critically Endangered” (Cabral et al. 2005) and besides an inherent heuristic nature, this work might draw attention towards the conservation of two narrow-range and highly confined fish species, while withdrawing useful cytogenetic comparative data against other members of the genus .

Material and methods

Adult specimens were captured by electrofishing in two distinct southern populations. Six (four males and two females) were collected in the Arade basin (OdePageBreaklouca River) and two (unknown sex) in the Mira basin (Torgal River). All procedures were developed in accordance to the recommended ethic guidelines (ASAB 2006). Some old chromosome images from material collected in the same drainages and studied by Collares-Pereira et al. (1998) were also reanalyzed (2 specimens of and 3 specimens of ) in order to confirm the results obtained with the new material. Chromosome spreads were obtained for one specimen using standard kidney protocol and for the remaining using fin fibroblast cultures (Rodrigues and Collares-Pereira 1996) to avoid fish sacrifice. Chromosome spreads were obtained by conventional splashing and selected for further cytogenetic analysis. Chromosomes were stained with a solution of 4% Giemsa (pH=6.8). CMA3 fluorescence staining was performed according to Sola et al. (1992), with a slide pre-wash in McIlvaine/MgCl2 buffer, one hour incubation with CMA3 (Calbiochem) and Methyl green counterstaining. Ag-NORs detection followed Howell and Black (1980) with modifications (Gold and Ellison 1983), using Giemsa counterstaining. Whenever possible, slides were destained and used in sequential treatments. The physical mapping of major rDNA gene cluster on the chromosomes was accomplished by FISH with rDNA probe. An rDNA clone containing 18S-5.8S-28S genes plus the intergenic spacers and untranscribed sequences from the genome of Meigen, 1830 (clone pDm 238, Rohia et al. 1981) was used as probe and labelled by nick translation with digoxigenin-11-dUTP according to the manufacturer’s specifications (Roche Applied Science). The probe was resuspended in hybridization mix composed of 50% ultra-pure formamide pH=7.5 (Sigma-Aldrich), 2× SSC and 10% (w/v) dextran sulfate powder (Sigma-Aldrich). Slides were denaturated in 70% formamide in 2× SSC at 65°C for 3 minutes, and immediately dehydrated in an ice-cold ethanol series (70%-90%-100%) for 7 minutes each and air-dried. The probe mixture was denatured at 75°C for 10 minutes, immediately placed on ice for another 10 minutes and added to the chromosome preparation. Hybridization was performed overnight in a dark moist chamber at 37°C. Post-hybridization washes were performed at room temperature (RT), for 7 minutes each: twice in 2× SSC and once in 2× SSC/0.1% Tween20. Slides were incubated with 3% bovine serum albumin (BSA) for 30 minutes at 37°C, in a dark moist chamber. Anti-digoxigenin antibody conjugated with fluorescein isothicyanate (FITC) (Roche Applied Science) was used to detect the probe for an hour and a half incubation at 37°C in a moist chamber. The slides were washed twice in 1x Phosphate Buffered Saline solution (PBS) at RT for 7 minutes and counterstained with DAPI in antifade solution. Slides were screened in an Olympus BX 60 epifluorescence microscope equipped with a DP50 Olympus CCD camera. All images were processed using Adobe Photoshop CS4 software. Chromosomes were arranged in a decreasing size order and classified according to their arm ratios (Levan et al. 1964) in three categories: metacentric (m), submetacentric (sm) and sub-telocentric to acrocentric (st/a). To determine the fundamental number (NF value), chromosomes of the m and sm groups were considered biarmed and those of group st/a as uniarmed.

Results

All and karyotypes revealed a diploid number of 2n = 50 chromosomes. Karyotypes of both and are composed of five pairs of metacentric (m), eighteen pairs of submetacentric (sm) and two pairs of subtelo/accrocentric (st/a) chromosomes. As the general karyotypes are the same for both species, only the results for using giemsa staining were included in Fig. 1. This genome composition leads to a high fundamental number (NF=96). As regards the eventual occurrence of heteromorphic sex chromosomes, no clear distinction between male and female karyotypes was observed in , the species where the specimens’ sex could be accurately assessed.
Figure 1.

a Giemsa stained metaphase and b corresponding karyotype of a male from Odelouca River (Arade drainage). Scale bar = 10µm.

The NORs’ phenotype was constant throughout all treatments, consistently positively labeling only one NORs-bearing chromosome pair likely homologous in both and species. Their rDNA-positive signals were co-localized to CMA3- and Ag-positive signals: in the short arm of a middle-size sm chromosome pair in both species as documented by sequential staining (Figs 2 and 3), indicative of being GC-rich and transcriptional active. No evidences of multi-chromosomal positive NOR’s signals were registered.
Figure 2.

Metaphase spreads of a male, stained with sequential treatments a rDNA FISH b CMA3-NOR, and c Ag-NOR treatments d corresponding karyotype of the same individual after rDNA FISH, with CMA3- and Ag-NOR signals inset. NORs are indicated by arrowheads. Scale bar = 10µm.

Figure 3.

Metaphase spreads of a , stained with sequential treatments a rDNA FISH b CMA3-NOR, and c Ag-NOR treatments d corresponding karyotype of the same individual after rDNA FISH, with CMA3- and Ag-NOR signals inset. NORs are indicated by arrowheads. Scale bar = 10µm.

a Giemsa stained metaphase and b corresponding karyotype of a male from Odelouca River (Arade drainage). Scale bar = 10µm. Metaphase spreads of a male, stained with sequential treatments a rDNA FISH b CMA3-NOR, and c Ag-NOR treatments d corresponding karyotype of the same individual after rDNA FISH, with CMA3- and Ag-NOR signals inset. NORs are indicated by arrowheads. Scale bar = 10µm. Metaphase spreads of a , stained with sequential treatments a rDNA FISH b CMA3-NOR, and c Ag-NOR treatments d corresponding karyotype of the same individual after rDNA FISH, with CMA3- and Ag-NOR signals inset. NORs are indicated by arrowheads. Scale bar = 10µm.

Discussion

and karyotypes display the general pattern described for most Leuciscinae: a diploid chromosome number of 2n = 50, a chromosome set with mainly bi-armed elements (dominated by submetacentrics with some metacentrics), and only one NOR-bearing chromosome pair. In cyprinids this is assumed to correspond to the ancestral character state and most likely represents also the synapomorphy for the genus (Ráb and Collares-Pereira 1995). A large subtelocentric/acrocentric PageBreakpair previously considered a chromosome marker for the subfamily (Ráb and Collares-Pereira 1995, Ráb et al. 2008) is also present in both species. The most common situation found in European Leuciscinae of a slightly higher number of st/a chromosomes might be due to the difficulty in obtaining high quality images for an accurate classification of chromosomes (Ráb and Collares-Pereira 1995, Collares-Pereira et al. 1998, Boron et al. 2009). The number and location of rDNA gene clusters have been used as chromosome markers in fish cytotaxonomy (e.g. Rábová et al. 2003, Boron et al. 2009, Kirtiklis et al. 2010, Pereira et al. 2012, Rossi et al. 2012). Conversely to what was reported in (Gromicho et al. 2005), no NORs polymorphism was observed in this study. Besides, Collares-Pereira et al. (1998) did not report any variation in NORs’ phenotype in all the populations analyzed. Karyotypes of these species conserved the plesiomorphic condition, where leuciscines have, in general, only one NOR-bearing chromosome pair (Ráb and Collares-Pereira 1995, Bianco et al. 2004, Luca et al. 2010, Rossi et al. 2012). Multiple NORs sites were detected in some individuals using 28S rDNA FISH mapping, presenting intra-individual variation and also failure in Ag-NOR in detecting most rDNA copies (Gromicho et al. 2005). However, those PageBreakobservations were made in specimens living in sympatry with the hybridogenetic complex (reviewed in Collares-Pereira and Coelho 2010) where hybridization is a recurrent process and might thus potentiate such variation in NORs. The karyotypes of the two species proved to be grossly similar at a macrostructural level. They are sister-taxa strongly clustered in many phylogenetic analyses, however consistently reciprocally monophyletic (Almada and Sousa-Santos 2010, Waap et al. 2011). Given their differentiation estimated at 7-8 MY ago (Doadrio and Carmona 2003, Sousa-Santos et al. 2007, Almada and Sousa-Santos 2010), perhaps more subtle chromosome differences will be found when new cytogenetic tools with a higher resolution will be operating in cyprinid’s chromosomes. The clear segregation of their lineage to the one including and is also consensual in phylogenetic analyses, and tree topology strongly supports them as basal members of the south-western Iberian lineage. Taking that into consideration, it is not surprising the conservation of the plesiomorphic state of the karyotype in both PageBreakand but their differentiation to the other two species living in Portuguese inland waters, respectively with 10–12m + 30–32sm + 8st/a for , and 12m + 32sm + 6st/a for (Collares-Pereira et al. 1998). Despite the apparent conservative pattern found in the two species here addressed by conventional cytogenetic tools, the karyotype variability present in the Iberian species of the genus so far analysed (Collares-Pereira et al. 1998, Gromicho et al. 2005), supports the occurrence of speciation processes favored by drastic changes in hydrological regimes (namely drought events), hence the difference between northern and southern populations. Whenever isolation and population bottlenecks occur, the sporadic mass reductions of population size might contribute to the stochastic fixation of chromosomal and genome mutations (Pereira et al. 2012). In particular, is geographically confined to a single intermittent river system and characterized by a very low level of genetic diversity (see also Almada and Sousa-Santos 2010, Henriques et al. 2010). Thus specific conservation measures have to be adopted if the option will be to preserve the genome integrity of this highly vulnerable species.
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