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Electronic Journal of Biotechnology

versão On-line ISSN 0717-3458

Electron. J. Biotechnol. vol.19 no.6 Valparaíso nov. 2016

 

RESEARCH ARTICLE

Expression analysis of vasa in Asian paddle crab (Charybdis japónica) exposed to Bisphenol A

 

Jianhua Chena,b,c,d*, Cuihua Wangb, Huan Gaoc,d, Binlun Yanc,d

a Jiangsu Marine Resources Development Research Institute, Huaihai Institute of Technology, Lianyungang 222005, China
b Key Laboratory of East China Sea & Oceanic Fishery Resources Exploitation and Utilization, Ministry of Agriculture, Shanghai 200090, China
c Jiangsu Key Laboratory of Marine Biotechnology, Huaihai Institute of Technology, Lianyungang 222005, China
d The Jiangsu Provincial Plat form for Conservation and Utilization of Agricultural Germplasm, Nanjing 2I00I4, China


ABSTRACT

Background: Bisphenol A (BPA) is an endocrine-disrupting chemical (EDC) with a weak estrogen-like activity in fish that is found ubiquitously in aquatic environments. However, there has been little study about BPA on the endocrine disrupting effects of crab. In the present study, cDNA of vasa was cloned and characterized in the Charybdis japonica. Histological structures of testis and expression patterns of vasa gene in the testis of C. japonica after treatment with BPA were investigated.

Results: The cDNA of vasa is composed of 3051 bp with a 2166 bp open reading frame encoding 721 AA. The deduced amino acid sequence contained eight conserved domains of the DEAD-box protein family. The tissue distribution showed that vasa mRNA was specifically expressed in ovary and testis. Histologically, the sperm cells were decreased in number and an acellular zone was seen in the testis. The transcript level of vasa gradually increased with a significant difference between the experimental and control groups. After BPA exposure with 0.50 and 1.00 mg/L for 1,3, 6 and 9 d, the expression levels of vasa increased. 

Conclusion: These findings suggest that BPA can increase the expression level of vasa mRNA and influence the development of the testis in C. japonica.

Keywords: Aquatic environments, BPA, DEAD-box, Endocrine disrupting, Expression analysis, Expression patterns, Histological observation, vasa, vasa cDNA, vasa gene, vasa mRNA.


 

1. Introduction

The effects of endocrine disrupting chemicals (EDCs) on normal reproduction and development of animals have received much attention. Xenoestrogen is a kind of common EDCs, pesticides and synthetic chemicals that have been reported to show a feminization effect, including Diazinon, Bisphenol A (BPA) and 4-nonylphenol (4-NP). Bisphenol A (BPA), existing widely in industrial wastewater, domestic sewage and sludge, is considered to be an endocrine disrupting chemicals (EDCs) with estrogen-like activity. In recent years, more reports have been made about the effects of BPA on the gonadal differentiation and developmental genes of aquatic organisms. The expression levels of both cyp19a and cyp19b were increased in Rivulus marmoratus exposed to 600 µg/L BPA and the male-specificgene dmrtl was down-regulated while the female-specificgene dax1 was up-regulated following BPA exposure in the mangrove killifish (Kryptolebias marmoratus).

DEAD-box protein is a family of ATP-dependent RNA helicase, which is widely found in species from bacteria to mammals. The DEAD-box protein family shared eight characteristic sequence motifs and participated in several vital cell processes, including RNA splicing, editing and processing, initiation of mRNA expression, nuclear export and degradation.

Vasa is one of the important members of the DEAD-box family, and was originally identified in Drosophila melanogaster,where it was considered to be a germ cell marker genes gene. Vasaplays an important role in the formation of germ cells, gametogenesis, establishment of polarity, and regulation of mRNA transcription in some developmental genes. Previous studies have shown that the vasa mRNA is specifically expressed in the germ cells of most species. Therefore, vasa is widely used as a molecular marker for gametogenesis and primordial germ cells (PGCs) origin, migration and differentiation, etc.

The differences of expression level of vasa mRNA was discovered in different stages of gametogenesis. In Spinibarbus caldwelli, the vasa mRNA was detected in each phase of the oogonia and oocytes, but the expression level of vasa was highest in the oogonia and was gradually reduced in all phases of ooctyes; during the spermatogenesis, vasa mRNA was detected in spermatogonia, but not in spermatocytes and spermatid. A similar phenomenon was observed in Carassius auratus gibelio.

The marine swimming crab Charybdis japonica (family Portunidae; infraorder Brachyura), is a common cave dweller in coastal areas, and widely distributed in China, Japan, Korea and Malaysia. Itisone of the most important marine crab species and has been cultured in the coastal areas of the Yellow & Bohai seas of China. In this paper, we isolated the cDNA sequence of vasa and investigate the characteristics of vasa expression of C. japonica after BPA exposure.

2. Materials and methods

2.1. Animals

Crabs (C. japonica) with an average mass of (56 ± 2.5) g were obtained from Aquatic Products Market of Lianyungang, Jiangsu Province, China. The crabs were acclimated to laboratory conditions for 7 d in fiberglass tanks, water temperature ranging from 20 to 22°C, water salinity of 27 ± 1%o. Crabs were fed fresh clam meat in three times each day.

2.2. Cloning of vasa cDNA and rapid-amplification ofcDNA ends (RACE)

Total RNA was isolated from gonads of crab using the TRIZOL reagent (Invitrogen) following the manufacturer's instructions. Reverse transcriptions were performed using Reverse Transcriptase M-MLV (TaKaRa) with the oligo (dT)18 primers according to the manufacturer's protocol.

The partial sequence of vasa cDNA was amplified with a pair of degenerate primers (Table 1), which were designed based on highly conserved domains of the known vasa sequences from previously reported crustaceans. The PCR was executed in the following conditions: 94°C for 3 min: 35 cycles of 94°C for 45 s, 58°C for 45 s, 72°C for 1.30 min; and 72°C for 10 min. The PCR products were electrophoresed on 1% agarose gel; the target DNA fragment was purified using a Gel Extraction kit (OMEGA) and then cloned into pMD18-T vectors (TaKaRa), and sequenced by Majorbio Company, Shanghai, China.

To obtain the full-length sequence of vasa, the rapid amplification of cDNA ends (RACE) was performed. A number of gene-specific primers (Table 1) were designed according to the vasa cDNA fragment obtained above. The 3'end of vasa was obtained in accordance with the manufacturer's instructions of 3'-Full RACE Core set ver. 2.0 (Takara, Japan). The extracting, purifying, and sequencing of the desired size fragments were performed as mentioned above.

Table 1
Primers used for fragment cloning, 5' and 3' RACE and qRT-PCR of vasa.

The 5' end of vasa was obtained according to a protocol described by Dieffenbach and Dveksler, where the primers (Table 1)for 5'RACE were designed based on the partial sequence of vasa cDNA. In brief, the first strand cDNA was synthesized with 2 µg total RNAas a template and V-5-R was the reverse primer using M-ML V reverse transcriptase (Promega). The cDNA was reacted with RNase H (MBI) and then a poly (A) tail was added at the 5' end using terminal deoxynucleotidyl transferase (MBI). The cDNA, containing the poly (A) tail was used as template for the first PCR. Amplification was performed with a universal forward primer Oligo (dT)16 AP and a specific reverse primer V-5-R1. The nested PCR, which used the first PCR product as a template, was carried out with a forward primer AP and a specific reserve primer V-5-R2. The extracting, purifying, and sequencing of the desired size fragment were performed as mentioned above.

2.3. Sequence analysis and alignment

The cDNA was analyzed using DNAstar7.0 and Vector NTI 10 (Invitrogen). The protein structures were predicted using online analysis tools such as ScanProsite (http://prosite.expasy.org/scanprosite), and the properties of the amino acid sequence was analyzed by the ExPASy ProtParam tool (http://www.expasy.ch/tools/protparam.html). Multiple alignments of the amino acid sequences were performed using the online tool in EMBL-EBI (http://www.ebi.ac.uk/Tools/msa/clustalw2/). The phylogenetic tree was generated using MEGA 4.0. The data was re-sampled by 1000 bootstrap replications to determine the confidence indices within the phylogenetic tree.

2.4. Expression analysis ofvasa mRNA in different tissues

To detect the vasa mRNA expression in different tissues, total RNA from heart, gills, intestine, hepatopancreas, muscle, testis and ovary was extracted using TRIZOL reagent (Invitrogen). The first strand of cDNA was synthesized with the oligo (dT)18. The primers (vasa-F1, vasa-R1) (Table 1) were used for analyzing vasa mRNA expression in different tissues. RT-PCR was run as follows: 94°C for 3 min; 30 cycles of 94°C for 45 s, 58°C for 45 s, 72°C for 30 s; and 10 min at 72°C for the ending extension. β-Actin was used as the preference gene (Table 1). The PCR was performed as follows: 94°C for 3 min; 22 cycles of 94°C for 45 s, 58°C for 45 s, 72°C for 30 s; followed by a final extension at 72°C for 10min.

2.5. BPA exposure and sample collection

BPA (≥99.0%) and β-estradiol (≥98.0%) were purchased from Sigma-Aldrich (St. Louis, MO, USA). A stock solution of BPA was prepared by dissolving solid in ethanol (analytical grade). Subsequently, the desired concentrations of BPA were prepared by diluting the stock solution in sea water.

Crabs were randomly divided into six groups, with each containing 36 individuals. Based on the results of the acute toxicity test in previous study of C. japonica exposure to BPA, four groups were tested at different concentrations of BPA (0.125, 0.25, 0.50 and 1.00 mg/L), with one control group (only ethanol) and a β-estradiol group (0.01 mg/L) as a positive control. All experiments were conducted in triplicate using independent samples. After 1, 3, 6, 9 and 15 d of BPA exposure, the testis of crabs from each group were frozen in liquid nitrogen immediately and stored at -80°C prior to the test of gene expression. Samples of testis from 1.00 mg/L BPA concentration group were fixed in Bouin's solution for light microscopic histological examination at d 15.

Fig.1.Nucleotide and deduced amino acidsequence of vasa in C. japonica. The Q-motifis shadowed. The eight conserved regions of the DEAD-box protein family and GG double tare boxed in black. RG and RGG repeats are underlined and double underlined, respectively. The two Zn-finger motifs (CCHC) are shown inside ovals.

2.6. Expression analysis ofvasa after BPA treatment

Real-time quantitative PCR (qRT-PCR) was carried out to determine the vasa expression of C. japonica exposed to BPA using the SYBR Green I chimeric fluorescence method. The qRT-PCR primers of vasa are listed in Table 1. The β-actin gene was used as the endogenous control (Table 1). The cycling program for the qRT-PCR was 95°C for 30 s, 40 cycles of 95°C for 5 s, 60°C for 30 s; followed by 95°C for 15 s, 60°C for 30 s, and 95°C for 15 s. The efficiency of the reactions was checked by analysis serial dilutions of cDNA. The calculation of the relative expression level of genes used the 2-ΔΔCt method.

2.7. Statistical analysis

Experimental data is shown as mean ± SEM. The data was analyzed with a one-way ANOVA, followed by Duncan's multiple comparison test, with p b  0.05 indicating a significant difference, using SPSS 16.0 for Windows.

3. Results

3.1. Molecular characterization ofvasa and sequence analysis

The full length cDNA of vasa was successfully acquired from C. japonica using RT-PCR and RACE methods. The size of the full cDNA of vasa (GenBank accession no. KF995354) was 3051 bp, which contained a 5'-untranslated region (UTR) of 100 bp, an open reading frame (ORF) of 2166 bp encoding a putative 721 AA (amino acid), and a3'-UTR of 785 bp. The predicted vasa protein has a calculated molecular weight of 77.14 kDa and a theoretical isoelectric point of 5.04. The deduced amino acid sequence contained eight conserved domains of the DEAD-box protein family, including AQTGSGKT (I), PTRELA (I a), TPGKL (I b), DEAD (II), SAT (III), LVFVE (IV), RGLD (V), HRIGRTGR (VI), and a GG doublet. In addition, EFPRPTPIQ (Q-motif) was present in 17 amino acids upstream of AQTGSGKT (I). Moreover, seven arginine-glycine repeats (RG) and, four arginine-glycine-glycine triad repeats (RGG) were present, with two zinc finger motifs (CCHC) in the N-terminus (Fig. 1).

Fig. 2. Phylogenetic tree based on a deduced amino acid alignment using the neighbor-joining method for VASA sequences in C. japonica and other vertebrates. C. japonica VASA are marked with a black triangular form. Numbers on nodes indicate bootstrap vales from 10,000 replicates.

Fig. 3. Tissue distribution of vasa expression in adult C. japonica by RT-PCR, O: ovary; T: testis; Gi: gill; He: hepatopancreas; In: intestines; M: muscle; H: heart.

3.2. Vasa sequence alignment and phylogenetic analysis

A comparison of the deduced amino acid sequence with those of other species ranging from invertebrates to vertebrates, revealed that the highest homology was shared with the green mud crab Scylla paramamosain (ACZ92304.1) and the Chinese mitten crab Eriocheir sinensis (ADM64419.1) (91.6-72.1% similarity). Low similarities were found with other species (b50%), such as Litopenaeus vannamei (AAY89069.2), Macrobrachium nipponense (AEQ19569.1), Apostichopus japonicas (ACA05234.1), Sus scrofa (AY626785.1), Homo sapiens (AY004154.1), Rattus norvegicus (AAB33364.1), Oncorhynchus mykiss (NP_001117665.1), and Danio rerio (AAI29276.1). Phylogenetic analysis showed that C. japonica VASA was more closely related to VASA homologs in other crabs, such as S. paramamosain and E. sinensis, compared to vertebrates, such as H. sapiens, Mus musculus (AFC17964.1), D. rerio, among others from the evolutionary process (Fig. 2).

3.3. Tissue-specific expression of vasamRNA

The distribution patterns of vasa in different tissues including ovary, testis, muscle, heart, intestine, gill and hepatopancreas of adult C. japonica were analyzed by RT-PCR. As shown in Fig. 3vasa mRNA was specifically expressed in the gonads and the expression, level of vasa in the ovary was higher than that in the testis. The expression of vasa mRNA was not detected in five other tissues that were tested.

3.4. Effect of BPA on histological structure ofthe C. japonica testis

Light microscopic sections of testis from C. japonica exposed to BPA are shown in Fig. 4. Compared to the control group, the amount of sperm cells was reduced and the acellular zone was observed in testis of C. japonica exposed to 1 mg/L BPA.

Fig. 4. Images of the testis of C. japonica exposed to BPA. (a): control group; (b): BPA treatment group. TP: Tunica Propria, Sp: Spermatocyte, AZ: Acellular Zone.

3.5. Expression analysis ofvasa mRNA in response to BPA

The expression level of vasa in the testis of C. japonica exhibited significant changes with exposure to BPA (Fig. 5). The vasa mRNA level in the group with a low concentration of BPA (0.125 mg/L) was maintained at a lower level without any significant difference from the control group. When crabs were exposed to 0.25 mg/L BPA for 9 and 15 d, the transcript level of vasa gradually increased with a significant difference from the control group. BPA exposures of 0.50 and 1.00 mg/L for 1, 3, 6 and 9 d led to gradually increased, expression levels of vasa, though a relative declined occurred after day 15. In the positive control group (E2), the vasa mRNA level was significantly higher than that of the control group.

4. Discussion

4.1. Characterization of vasa

The DEAD box protein family is ATP-dependent RNA helicases, which has eight conserved domains. In the present study, the full-length vasa cDNA of C. japonica was acquired, and like other species, the deduced amino acid sequence of C. japonica had eight conserved domains. In addition, a glycine-rich region in the N-terminus and multiple RGG repeats were observed in C. japonica Vasa, which is similar to the Vasa structure described in previous studies. The RGG/RG motifs in the N-terminus are considered to be associated with RNA binding. The zinc finger motifs (CCHC) were also observed in the N-terminus of C. japonica Vasa, which may have an effect on binding with nucleic acid. These results suggest that the vasa gene is relatively conserved for the protein structure, implying that it has a unique biological function for the DEAD-box family proteins.

4.2. Tissue distribution ofvasa mRNA

In previous studies, vasa mRNA was shown to be highly expressed in ovary and testis, whereas its expression was very weak in other tissues. In crustaceans, the vasa of the mud crab S. paramamosain was expressed only in the ovary and testis. Similar results were observed in M. nipponense. In the present study, the vasa were specifically expressed only in ovary and testis of C. japonica, which is consistent with previous studies. vasa gene likely plays an important role in oogenesis and spermatogenesis of C. japonica.

Fig. 5. Relative expression level of vasa in testis of C. japonica after exposure to BPA using quantitative real-time RT-PCR and beta-actin as an internal standard. Data are presented as mean ± SEM (n = 6). Note: * in column diagram indicates significant difference (p b 0.05) among the groups at the same test time.

4.3. Effect of BPA on the histological structure of C. japonica

Previous studies have shown that some EDCs, such as nonylphenol (NP), BPA and estradiol (E2), can cause changes in the structure of testis from the zebrafish. In the present study, a large number of acellular zones were noted in testis tissue of C. japonica after exposure to 1 mg/L BPA and the number of spermatocytes was also reduced. These observations are consistent with those of previous studies by Cao et al. and Liu et al. in the zebrafish exposed to BPA and NP, respectively.

4.4. Expression characteristics ofvasa after exposure to BPA

The vasa gene is a specific marker for primordial germ cells (PGCs) in fish and plays a vital role in generation, migration, differentiation, and maturation of PGCs. Numerous experiments have demonstrated that some EDCs in the environment have feminizating effects on fish and effectsonPGCsand the vasa gene. Cardinali et al. reported that the expression level of vasa was increased in Sparus autata exposed to E2. Moreover, the expression level of vasa was reported to be significantly up-regulated in D. rerio exposed to monocrotophos (unpublished data). Regarding the increasing expression of vasa induced by EDCs, two views have been put forward as explanations: 1) EDCs enhance the expression of vasa in the existing germ cells, and 2) the number of germ cells-specifically expressing vasa increases. Moreover, Hoshi et al. reported that the number of germ cells was significantly increased in Caenorhabditis elegans exposed to E2 and BPA. In the present study, the vasa level was increased in the testis of C. japonica after exposure to BPA. This is consistent with the findings for S. autata after exposure to E2 and D. rerio after exposure to monocrotophos, which was considered to be due to the increase in number of germ cells (unpublished data). Nevertheless, from observations of microstructure, the number of germ cells appeared to be decreased in C. japonica after exposure to BPA, and thus, the explanation would be that the increase in vasa expression due to the rise in vasa expression in the existing germ cells.

5. Concluding remarks

In the present study, cDNA of vasa from C. japonica was isolated and the expression level of vasa was identified after exposure to BPA. The change in the histological structure was also investigated. After exposure to BPA, the number of sperm cells was reduced along with testis degeneration. The vasa mRNA was specifically expressed in ovary and testis, and the expression level of vasa was increased after BPA exposure. These findings suggest that BPA can increase the expression level of vasa mRNA and influence the development of the testis in C. japonica.

Financial support

This work was supported by the Priority Academic Program Development of Jiangsu Higher Education Institutions (PAPD) (5511201401X), Open Foundation of key laboratory of East China Sea & Oceanic Fishery Resources Exploitation and Utilization, Ministry of Agriculture, P.R. China (Grant No. K201210), and Science and Technology Planning Project of Lianyungang City (CN1410). We also thank anonymous reviews and the Assistant Editor for providing valuable comments on the manuscript.

Conflict of interest

We declare that we have no conflict of interest.

 

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Article history: Received 7 July 2016 Accepted 6 October 2016 Available online 19 October 2016

* Corresponding author at: Jiangsu Marine Resources Development Research Institute, Huaihai Institute of Technology, Lianyungang, 222005, China. E-mail address: chenjianhuazsu@163.com (J. Chen).

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