This article was published in an Elsevier journal. The attached copy is furnished to the author for non-commercial research and education use, including for instruction at the author’s institution, sharing with colleagues and providing to institution administration. Other uses, including reproduction and distribution, or selling or licensing copies, or posting to personal, institutional or third party websites are prohibited. In most cases authors are permitted to post their version of the article (e.g. in Word or Tex form) to their personal website or institutional repository. Authors requiring further information regarding Elsevier’s archiving and manuscript policies are encouraged to visit: http://www.elsevier.com/copyright Author's personal copy Aquatic Toxicology 86 (2008) 131–141 Development of a marine fish model for studying in vivo molecular responses in ecotoxicology R.Y.C. Kong a , J.P. Giesy a,b , R.S.S. Wu a , E.X.H. Chen a , M.W.L. Chiang a , P.L. Lim c , B.B.H. Yuen a , B.W.P. Yip a , H.O.L. Mok a , D.W.T. Au a,∗ a b Centre for Coastal Pollution and Conservation, City University of Hong Kong, 83 Tat Chee Avenue, Kowloon, Hong Kong Department of Veterinary Biomedical Sciences & Toxicology Center, University of Saskatchewan, Saskatoon, SK, Canada c Clinical Immunology Unit, Prince of Wales Hospital, The Chinese University of Hong Kong, Shatin, Hong Kong Received 15 August 2007; received in revised form 16 October 2007; accepted 19 October 2007 Abstract A protocol for fixation and processing of whole adult marine medaka (Oryzias melastigma) was developed in parallel with in situ hybridization (ISH) and immunohistochemistry (IHC) for molecular analysis of in vivo gene and protein responses in fish. Over 200 serial sagittal sections (5 m) can be produced from a single adult medaka to facilitate simultaneous localization and quantification of gene-specific mRNAs and proteins in different tissues and subcellular compartments of a single fish. Stereological analysis (as measured by volume density, Vv ) was used to quantify ISH and IHC signals on tissue sections. Using the telomerase reverse transcriptase (omTERT) gene, omTERT and proliferating cell nuclear antigen (PCNA) proteins as examples, we demonstrated that it is possible to localize, quantify and correlate their tissue expression profiles in a whole fish system. Using chronic hypoxia (1.8 ± 0.2 mg O2 L−1 for 3 months) as an environmental stressor, we were able to identify significant alterations in levels of omTERT mRNA, omTERT protein, PCNA (cell proliferation marker) and TUNEL (apoptosis) in livers of hypoxic O. melastigma (p < 0.05). Overall, the results suggest that O. melastigma can serve as a model marine fish for assessing multiple in vivo molecular responses to stresses in the marine environment. © 2007 Elsevier B.V. All rights reserved. Keywords: Hypoxic stress; Histology; Immunohistochemistry; ISH; Telomerase 1. Introduction A variety of molecular, biochemical and histological responses in fish have been employed as biomarkers of various environmental stresses (Gavilán et al., 2001; Au, 2004; Facey et al., 2005; Hutchinson et al., 2006). While these suborganismal responses are sensitive, reproducible and easier to determine, most of them are tissue- and/or cell-specific. For instance, CYP1A1 mRNA expression and EROD enzyme induction are different in liver (hepatocytes), intestine (enterocytes) and gill (epithelia) of fish, depending on the exposure route of toxicants (Wong et al., 2001; Yuen and Au, 2006). Current molecular techniques such as real-time PCR and Western blotting and chemical analysis of metabolites normally only provide information for individual tissues or the whole animal, but are ∗ Corresponding author. Tel.: +852 2788 971; fax: +852 2788 7406. E-mail address: bhdwtau@cityu.edu.hk (D.W.T. Au). 0166-445X/$ – see front matter © 2007 Elsevier B.V. All rights reserved. doi:10.1016/j.aquatox.2007.10.011 unable to differentiate molecular changes among different cell types within the tissue. Recently, there is a trend of using small size fish as sentinel vertebrate species for ecotoxicology and biomedical research (Moore, 2002; Wittbrodt et al., 2002; Hawkins et al., 2003; Hinton et al., 2005). Small fish have several advantages in ecotoxicological studies, since they are generally easy to maintain and breed under laboratory conditions. The generation time is relatively short, and fish can produce eggs regularly, hence providing a variety of developmental and reproductive endpoints for whole life cycle and multi-generation assessments. To this end, the zebrafish (Danio rerio), fathead minnow (Pimephales promelas), mosquito fish (Gambusia affinis), guppy (Poecilia reticulata) and Japanese medaka (Oryzias latipes) have been commonly used as freshwater fish models in ecotoxicological studies (Dodd et al., 2000; Castro et al., 2004; Wolf et al., 2004; Volz et al., 2005; Carter and Wilson, 2006; Kissling et al., 2006). Surprisingly, a fish model for assessing environmental stress in the marine environment has not been developed, although Author's personal copy 132 R.Y.C. Kong et al. / Aquatic Toxicology 86 (2008) 131–141 a number of freshwater/estuarine species (e.g. the sheepshead minnow Cyprinodon variegatus and the mummichog Fundulus heteroclitus) has also been commonly adapted to seawater for toxicological studies due to their hardiness in captivity. However, both C. variegatus and F. heteroclitus suffer from varying rates of growth, which compromises equilibrating toxic responses, and poor knowledge of their genomes make molecular toxicological studies on these species difficult. Further, the mummichog takes 2 years to reach sexual maturity, and this makes it difficult to carry out whole life cycle studies. The marine medaka Oryzias melastigma (McClelland) has a number of attributes that render it a potentially good marine fish for ecotoxicological studies. O. melastigma is small and easy to culture and breed, and it completes the whole life cycle in seawater. Marine medaka are similar to freshwater medaka O. latipes, they exhibit uniform growth, which confer an additional advantage in using this species for ecotoxicological studies. Phylogenetically, this species is closely related to O. latipes, of which the entire genome has been worked out recently (Kasahara et al., 2007). The anatomy, biology and nutritional requirements of O. melastigma is similar to that of O. latipes, which are well known and an atlas is available (Anken and Bourrat, 1998; Fujita et al., 2006). In addition, much of the information on the physiology of O. latipes (http://www.bio.nagoya-u.ac.jp:8000/Welcome.html) is also applicable for O. melastigma. Notwithstanding, the use of small fishes for tissue-specific molecular analyses presents a major challenge. The quantity of a specific tissue available for analysis is often very limited, and isolation of such a small amount of tissue is often difficult and time consuming. However, this limitation can be overcome by using in situ hybridization (ISH) and immunohistochemistry (IHC) analyses on preserved whole fish tissues. With the recent advent of image analysis software, the effectiveness of stereological analysis for quantification of IHC and ISH signals on tissue sections has been greatly enhanced. Moreover, various technical problems are associated with the fixation and sectioning of relatively large-sized adult fish specimens (ca. 3 mm) (Weber et al., 2002), due mainly to its heavy bony structures. Traditional decalcification of bony structures using formic acid or EDTA not only lead to poor RNA preservation, but are also time consuming (and may require up to 7 days) (Moore et al., 2002). Previous fixation protocols for adult small fish, e.g. the Japanese medaka, zebrafish, guppy and mosquito fish were specifically designed for histopathologic evaluation (Fournie et al., 1996; Neely et al., 2002; Zodrow et al., 2004) and a few on immuno-localization studies (Ortego et al., 1994; Moore et al., 2002; Ko et al., 2005). Until now, no protocols have been developed for the parallel detection of mRNA and protein molecules in whole tissues of these adult small fish. In the first part of this study, we have developed and optimized procedures for the fixation and processing of whole adult marine medaka, enabling the production of tissue sections suitable both for subsequent ISH and IHC analyses. Telomerase is an enzyme involved in cell immortalization, carcinogenesis and tissue regeneration (Greider, 1998). The catalytic subunit telomerase reverse transcriptase (TERT) has been shown to regulate cell proliferation, mediate apoptosis, promote DNA repair and cell survival in vitro (see review of Chung et al., 2005), which suggest that TERT has a central role in controlling in vivo cell growth and tissue homeostasis. In fish, expression of TERT gene has been found in a variety of somatic tissues in O. melastigma (Yu et al., 2006) and Fugu rubripes (Yap et al., 2005). In the second part of this study, we employed the omTERT mRNA and protein and proliferating cell nuclear antigen (marker for cell proliferation) as molecular endpoints to demonstrate the feasibility of using ISH and IHC techniques to simultaneously localize and measure in vivo expression levels of these gene and proteins in different tissues of a single medaka fish, and to allow statistical analysis to be made on the correlation of these gene and protein expression data in a whole fish. Hypoxia has now become a pressing environmental problem in aquatic systems worldwide (Diaz, 2001; Wu, 2002). Hypoxia has been reported to up-regulate TERT expression in liver of O. melastigma (through the hypoxia-inducible factor-1, HIF-1) (Yu et al., 2006), which may perturb normal cell proliferation and apoptosis in hepatocytes. In the third part of this report, we used hypoxia as a model stressor and the liver as a model organ to study the stress responses of omTERT mRNA (by ISH) and protein (by IHC), cell proliferation (by PCNA) and apoptosis (by the terminal dideoxynucleotidyl-mediated dUTP nick end labeling, TUNEL) in O. melastigma. The overall objective of this study is to demonstrate that O. melastigma can serve as a good marine fish model for ecotoxicology, and enable in vivo molecular responses at the nucleic acid and protein levels to be localized and measured simultaneously in different tissues/cells of the same individual. 2. Materials and methods 2.1. Marine medaka Marine medaka were purchased from a commercial hatchery in Taiwan and were maintained in 30‰ artificial seawater at 5.8 ± 0.2 mg O2 L−1 , 28 ± 2 ◦ C in a 14-h light:10-h dark cycle. Under optimal growth and breeding conditions, adult O. melastigma produced sufficient numbers of genetically homogeneous offspring. For the chronic hypoxia exposure experiment, 4-week old O. melastigma were used and divided into two groups. The first group was maintained in a hypoxic system (1.8 ± 0.2 mg O2 L−1 ) and the second group under normoxia (6.4 ± 0.2 mg O2 L−1 ). Dissolved oxygen was monitored continuously using DO meters and polarographic probes (ColeParmer 5643-00, IL, USA). A detail design of the hypoxic and normoxic systems is given in Shang et al. (2006). At the end of a 3-month exposure period, whole adult O. melastigma were fixed and processed for parallel analyses by ISH (omTERT gene), IHC (TERT protein and PCNA) and TUNEL (apoptosis). 2.2. Fixation and processing of whole adult O. melastigma Adult O. melastigma (ca. 3.5 in cm length) were immobilized in ice-chilled water. Fixative was flushed over the gills and injected into the abdominal cavity through the mouth using a Author's personal copy R.Y.C. Kong et al. / Aquatic Toxicology 86 (2008) 131–141 133 Table 1 Summary of fixation and processing regimes for histological and molecular analyses of whole adult O. melastigma Trials Fixation (overnight at 4 ◦ C) Clearing medium Processing temperature Evaluation Sectioning quality Morphology Labeling efficiency IHC ISH 1 4% PFA in 0.1 M CB 4% PFA in PBS 1:1 8% PFA:NSW Xylene Xylene Xylene RT RT RT Poor Poor Poor Good Moderate Poor n.d. n.d. n.d. n.d. n.d. n.d. 2 HC HC with 1% sucrose HC with 5% sucrose HC with 10% sucrose Xylene Xylene Xylene Xylene RT RT RT RT Good Good Good Good Poor Moderate Moderate Poor n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. 4% PFA in 0.1 M CB followed by HC with 1% sucrose 2% PFA & 2.5% Glut in 0.1 M CB followed by HC with 1% sucrose 4% PFA in 80% HC with 1% sucrose Chloroform RT Moderate Good n.d. n.d. Chloroform RT Moderate Best n.d. n.d. Chloroform RT Good Good n.d. n.d. Chloroform 4 ◦C Best Best n.d. n.d. Chloroform 4 ◦C Best Best Good n.d. Chloroform 4 ◦C Best Best Best Good Chloroform 4 ◦C Best Best Best Best 3 4 5 2% PFA and 0.2% Glut in 80% HC with 1% sucrose 2% PFA and 0.05% Glut in 80% HC with 1% sucrose 2% PFA and 0.05% Glut in 80% HC with 1% sucrose and 1% CaCl2 2% PFA and 0.05% Glut in 80% HC with 1% sucrose and 1% CaCl2 followed by infiltration in gum sucrose PFA, Paraformaldehyde; CB, cacodylate buffer; PBS, phosphate-buffered saline; NSW, natural seawater; HC, HistoChoice; Glut, glutaraldehyde; n.d., not determined. small syringe. A small hole was punched into the swim bladder through the mid-dorsal body wall with a fine pin, and the body was gently pressed to release the gas. The body was slit open along the mid-ventral line (from the anal vent to the operculum) to facilitate rapid penetration of the fixative. Hard tissues (including skull roof, otoliths, operculum and fins) were gently removed and fish were immersed in fixatives overnight at 4 ◦ C (Table 1). Fixed fish were dehydrated in a 70/80/95/100% graded series of methanol (20 min × 2) followed by clearing in chloroform (30 min × 3 and 15 min × 2) at 4 ◦ C. All processing steps (from fixation to clearing) were conducted in a tissue rotator (FINEPCR, Korea) at 10 rpm. Dehydrated O. melastigma were infiltrated for 2 h (30 min × 4) at 55 ◦ C in melted paraffin (Paraplast X-TRA from Tyco Healthcare, UK) before embedding. Fish were orientated diagonally inside an embedding mold (EMS, USA) with the head pointing toward the bottom lefthand corner of the mold. Solidified blocks were stored at 4 ◦ C until ready to use. Serial sagittal sections (5 m) were cut on a rotary microtome (Leica RM2125, Germany) and mounted onto Superfrost® Plus slides (Menzel-Gläser, Germany). All sections collected from a single fish were number-coded for subsequent ISH and IHC experiments. Tissue sections were dried overnight on a slide warmer at 37 ◦ C before analyses. 2.3. Whole fish in situ hybridization A 300-bp omTERT fragment spanning motif E and motif E-I (nt. 2749–3048; Yu et al., 2006) was cloned into the pGEM- T Easy vector (Promega, Madison, USA), and digoxigenin (DIG)-labeled antisense and sense riboprobes were synthesized by in vitro transcription. Deparaffinized and rehydrated O. melastigma tissue sections were digested with proteinase K (1 mg mL−1 ) at room temperature for 20 min and post-fixed in 4% paraformaldehyde in PBS for 20 min. Hybridization was performed overnight at 50 ◦ C with DIG-labeled riboprobes (0.5 ng L−1 ) in 2× SSC, 50% formamide, 10% dextran sulfate, 50 g mL−1 yeast tRNA and 5 U mL−1 RNase inhibitor. After hybridization, slides were washed in a graded series of SSC, 0.1% Tween 20 at room temperature and incubated with antiDIG antibody coupled to alkaline phosphatase (at 1:100 dilution; Roche Applied Science, Germany). Signals were detected using the NBT/BCIP substrate (Zymed, South San Francisco, USA). Sections were counterstained with Nuclear Fast Red and then examined by light microscopy (Axioplan 2 imaging; Carl Zeiss, Germany). 2.4. Western blotting Cytoplasmic and nuclear proteins were extracted from adult fish organs (gill, liver, kidney and intestine, testes, ovary, brain and muscle) using NE-PER® Nuclear and Cytoplasmic Extraction Reagents (Pierce Biotechnology, Rockford, USA) according to the manufacturer’s instructions. Each organ from 5 to 10 fish was pooled for protein extraction. Cytoplasmic and nuclear proteins (10–40 g) were separated in 7% SDS PAGE, transferred to PVDF membranes (GE Healthcare Bio- Author's personal copy 134 R.Y.C. Kong et al. / Aquatic Toxicology 86 (2008) 131–141 Sciences, NJ, USA), blocked in 5% non-fat dry milk (Nestle, Shuangcheng, People’s Republic of China) in 0.1% TPBS (0.1% Tween 20 in 0.1 M Na2 HPO4 , 0.1 M NaH2 PO4 , 0.5 M NaCl, pH 7.2) and incubated overnight at 4 ◦ C with mouse antihuman TERT monoclonal antibody mAb476 (1:1000) (Leung et al., 2005). Non-specific binding of antibody was washed off with three changes of 0.1% TPBS followed by detection with HRP-conjugated secondary anti-mouse IgG (1:5000 dilution in 5% non-fat milk in 0.1% TPBS) at room temperature for 1 h. After washing with three rounds of 0.1% TPBS, the signal was detected with ECL Plus Western Blotting Detection System (GC Healthcare) and the membranes were exposed to HyperfilmTM ECLTM (GE Healthcare). 2.5. Immunohistochemistry (omTERT and PCNA) Deparaffinized and rehydrated O. melastigma tissue sections were incubated for 15 min in 100% methanol containing 0.03% H2 O2 to quench endogenous peroxidases. For immunolocalization of omTERT protein, antigen retrieval in Enhancing buffer (IDL Biotech, Bromma, Sweden) for 20 min was followed by incubation with anti-hTERT monoclonal antibody mAb476 (1:100 diluted) (Leung et al., 2005) at room temperature for 2 h. For PCNA staining, after heat retrieval by microwave in citrate buffer (pH 6.0) for 15 min, fish sections were incubated with monoclonal antibody (no. M0879) for PCNA antigen (1:5000; DakoCytomation, Denmark) at room temperature for 1 h. For both omTERT and PCNA staining, treatment with the primary antibodies were followed by incubation with HRP-conjugated secondary goat anti-mouse IgG antibody (1:5000 dilution in 1% BSA in PBS; Dako EnvisionTM + System, Denmark) at room temperature for 30 min. Sections were rinsed in PBS and signals detected with the chromogenic substrate, 3,3 -diaminobenzidine chromogen (DAB) (DakoCytomation, Denmark). Sections were counterstained with Mayer’s Hematoxylin (DakoCytomation, Denmark) and mounted using Permount (Fisher Scientific). Negative controls were prepared by substitution of the primary antibody with non-immune sera. 2.6. TUNEL assay Apoptotic cell death was determined using terminal dideoxynucleotidyl-mediated dUTP nick end labeling (TUNEL) according to the manufacturer’s instructions (Roche Applied Science, Germany). Tissue sections on slides were rinsed with PBS, incubated in permeabilization solution (0.1% Triton X100 and 0.1% sodium citrate) for 2 min on ice, rinsed twice with PBS, incubated with 10 l TUNEL reaction mixture (terminal deoxynucleotidyl transferase 200 U mL−1 , FITC-labeled dUTP 10 mM, 25 mM Tris–HCl, 200 mM sodium cacodylate, 5 mM cobalt chloride) for 60 min at 37 ◦ C, and then rinsed 3× with PBS. For visualization of TUNEL signals, tissue sections were incubated with 10 l Converter-POD (anti-FITC antibody, Fab fragment from sheep, conjugated with horseradish peroxidase) for 30 min, rinsed 3× with PBS, and then stained with DABsubstrate solution (DakoCytomation, Denmark) for 10 min in the dark at room temperature. Negative control was obtained by omitting TdT from the TUNEL reaction mixture. Sections were counterstained with Mayer’s hematoxylin (DakoCytomation, Denmark) for 2 min and a cover slip was mounted with a drop of pure Permount® (Fisher Chemical, USA). Only the brown and condensed nuclei with fragmented nucleoli showing the characteristic apoptotic morphology were counted as apoptotic nucleus. 2.7. Stereological analysis Expression of omTERT mRNA and protein, PCNA and TUNEL signals were measured by volume density (Vv ), according to the stereological principles of Weibel (1979) and Reed and Howard (1998). Vv represents the volume fraction of positively stained cells in the fish target tissue and was calculated according to Eq. (1): Vv = Pi PT (1) where Pi is the number of test points enclosed within the profiles of the particulate structure investigated (i.e., omTERT mRNA Table 2 Stereological quantification of omTERT, PCNA and TUNEL positive signals in tissues of adult O. melastigma detected by ISH and IHC Organ Fish replicates Magnification Test system, d (m) Number of test points Number of fields for analysis Stereological parameter: volume density, Vv (Pi , reference space) Gonad Testis 5 males 200× Square lattice, d = 20 192 (16 × 12) Vv (positive signals, sperm cysts) 5 females 200× Square lattice, d = 20 192 (16 × 12) Kidney Intestine 5 males/5 females 5 males/5 females 600× 600× Square lattice, d = 5 Square lattice, d = 5 432 (24 × 18) 432 (24 × 18) Whole organ on section Whole organ on section 15 10 Gill 5 males/5 females 600× Square lattice, d = 5 432 (24 × 18) 15 Liver 5 males/5 females 600× Square lattice, d = 5 432 (24 × 18) 10 Muscle 5 males/5 females 600× Square lattice, d = 5 432 (24 × 18) 30 Ovary Vv (positive signals, ovarian follicles) Vv (positive stained nuclei, kidney) Vv (positive stained nuclei, intestinal epithelia) Vv (positive stained nuclei, gill filament and lamella) Vv (positive stained nuclei, liver parenchyma) Vv (positive stained nuclei, muscle fibres) Author's personal copy R.Y.C. Kong et al. / Aquatic Toxicology 86 (2008) 131–141 135 Fig. 1. omTERT immunostaining patterns in sagittal sections of whole adult (16-week old) marine medaka, O. melastigma. Immunohistochemistry was performed using anti-human TERT monoclonal antibody on male (A) and female (B) fish sections, and signal detection was accomplished with diaminobenzidine (DAB). (Sections were counterstained with hematoxylin.) Br, Brain; Bb, backbone; E, eye; G, gill; Gb, gall bladder; Gu, gut; H, heart; K, kidney; L, liver; M, muscle; O, ovary; Sb, swimming bladder; Sc, spinal cord; T, testis. Scale bar = 2 mm. (Insets) External morphologies of fish of the respective sex. and protein, PCNA or TUNEL-positive signals) and PT is the number of test points falling on the reference space (i.e., the fish tissue being investigated). Stereological analysis was performed on each fish tissue with the aid of the Computer Assisted Stereology Toolbox (CAST) 2.0 software (Olympus, Denmark). Images were captured using the Olympus BX51 compound microscope (Denmark) equipped with a motorized stage (ProScan; PRIOR Scientific, USA) and a 3-CCD color video camera (KY-F58; JVC, Japan). The stereological procedures for quantitative ISH and IHC analyses are summarized in Table 2. 2.8. Statistical analyses Pearson product-moment correlation analysis was used to relate the in vivo expression levels of omTERT mRNA and protein, and their relationships to PCNA in gonad, kidney, intestine, gill, liver and muscle of the same fish (n = 5 for each sex). Student’s t-test was used to test the null hypothesis that there were no quantitative changes in particulate expression levels (Vv of omTERT mRNA-, omTERT protein-, PCNA- and TUNEL-positive stained nuclei) between the normoxic control and hypoxic samples. Significance level (α) was set at 0.05 (Zar, 1996). 3. Results 3.1. Whole adult O. melastigma fixation and processing The protocol that yielded high quality tissue sections with optimal preservation of tissue and cellular morphology, nucleic acid and antigenicity was developed by optimizing various fixation and processing regimes that included testing the efficacy of: (i) fixative combinations; (ii) clearing media and (iii) processing temperatures (Table 1). Among all of the conditions tested, primary fixation of adult O. melastigma in a cocktail of 0.05% glutaraldehyde (Glut), 2% paraformaldehyde (PFA) Fig. 2. Subcellular localization of omTERT protein in different tissues of adult O. melastigma. Western blot analysis of omTERT was performed on cytoplasmic (Cy) and nuclear (Nu) fractions from representative reproductive (A), somatic (B) and regenerative (C) tissues of adult O. melastigma (4-month old). Author's personal copy 136 R.Y.C. Kong et al. / Aquatic Toxicology 86 (2008) 131–141 Fig. 3. Parallel in situ hybridization and immunohistochemical staining patterns for omTERT mRNA, omTERT protein and PCNA in reproductive (testis and ovary) (A–F), somatic (brain and muscle) (G–L) and regenerative (gill, intestine, kidney and liver) (M–X) tissues of O. melastigma. Serial sections in the left column were hybridized with omTERT antisense riboprobe and immunodetected with anti-DIG antibody coupled to alkaline phosphatase. Signals were visualized using NBT/BCIP as substrate (purple, positive signal). Sections were counterstained with nuclear fast red (red, negative signal). Sections in the middle and right columns Author's personal copy R.Y.C. Kong et al. / Aquatic Toxicology 86 (2008) 131–141 and 1% sucrose and 1% CaCl2 in Amresco® HistoChoiceTM MB for 16 h at 4 ◦ C, followed by immersion in Holt’s gum sucrose solution (1% aqueous gum arabic [Sigma, St. Louis, USA] and 30% aqueous sucrose) (Holt et al., 1960) at 4 ◦ C for 24 h yielded the best results in section quality and preservation of tissue morphology, nuclei acid and antigenicity (Table 1). Because xylene rendered fish tissues too brittle for sectioning, chloroform was used instead as the clearing agent. Likewise, PFA fixation is generally favorable for the preservation of tissue and cellular morphology but poor for sectioning owing to tissue brittleness, and hence HistoChoice (HC) was used to soften bony tissues, rendering the fixed adult fish easier to section, and no decalcification step (in formic acid, EDTA) was required. Fixation of whole adult fish in a cocktail of HC with 1% sucrose in 2% PFA and 0.05% Glut at 4 ◦ C considerably improved tissue preservation and sectioning quality without weakening IHC labeling efficiency. Fatty tissues were better preserved by low-temperature processing. Infiltration of fixed whole fish tissues in gum-sucrose overnight at 4 ◦ C further enhanced tissue preservation as well as efficiency of ISH and IHC labeling. The quality of tissue preservation using this regime was equally satisfactory for both male (Fig. 1A) and female fish (Fig. 1B). By and large, at least 200 serial sagittal whole fish sections could be obtained from a single fish allowing multiple fish organs/tissues to be examined simultaneously on a single section for parallel histological evaluation and quantitative mRNA/protein localization after ISH/IHC, respectively (Fig. 1A and B). 3.2. Western blotting Specific hybridization of the mouse anti-human TERT monoclonal antibody (mAb476) to the medaka omTERT protein (expected size of 120 kDa) was detected in nuclear extracts from gill, liver, testes, brain and muscle tissues of O. melastigma (Fig. 2). However, no protein band of 120 kDa in size was detected in extracts from fish kidney, intestine and ovary. Sequence alignment of the hTERT protein at aa 543–668 (region recognized by mAB476) with the corresponding region in the omTERT protein (aa 507–621) showed high sequence similarity (53%) between the human and fish sequence. 3.3. Tissue-specific expression revealed by ISH and IHC on whole fish sections ISH using DIG-labeled antisense riboprobes revealed distinct localization patterns of omTERT mRNA in various 137 organs of adult O. melastigma. No hybridization signal was observed in fish tissues with the sense omTERT riboprobe (negative control). Similarly, immunoreactivity of the mAb476 and M0879 antibodies for the omTERT protein and PCNA, respectively, are cell-type specific although differences in subcellular distribution patterns were observed for the two proteins (Fig. 3A–X). No immunoreactivity was observed in fish tissues with non-immune sera in the negative controls. In testis, high expression of omTERT mRNA (ISH), and strong omTERT protein and PCNA immunoreactivity were detected in dividing spermatogonia (Sg), spermatocytes (Sc) and spermatids (St), but not in differentiated spermatozoa (Sz) (Fig. 3A–C). In ovary, strong expression of omTERT mRNA was detected in the cytoplasm of pre-vitellogenic (PV) oocytes (Fig. 3D–F), while omTERT protein and PCNA were localized in the nuclei of PV oocytes and granulosa cells of vitellogenic oocytes. In brain, while both omTERT mRNA and omTERT protein were detected in the granule cell mass of telencephalon, optic tectum and cerebellum (Fig. 3G–I), with intense omTERT immunostaining being observed in the cytoplasm; PCNA-positive cells were clearly evident at the borders between the telencephalon and diencephalon, and between the mesencephalon and rhombencephalon, which are the proliferative zones of the brain. In muscle, omTERT mRNA was only weakly expressed (Fig. 3J), with omTERT protein and PCNA immunostaining being detected only in the nuclei of fibroblasts and muscle fibers (Fig. 3K and L). The relative abundance of PCNA-positive cells was less than those that showed positive immunoreactivity for the omTERT protein. In gill, PCNA-positive cells and cells expressing omTERT mRNA were localized along the epithelial filaments of the gill (Fig. 3M–O), while cells showing omTERT immunoreactivity were evident in the epithelia of both gill filaments and lamellae. In intestine, expression of omTERT mRNA and protein were detectable in enterocytes of the mucosal epithelia (Fig. 3P–R), whereas PCNA staining was confined to the nuclei of proliferative enterocytes near the crypt region of the mucosal folds. In kidney, omTERT mRNA was only modestly expressed (Fig. 3S–U) while omTERT immunostaining was most prominent in renal epithelial cells (both nucleus and cytoplasm) and in the adjoining lymphoid tissues. PCNA immunostaining was strong in lymphoid tissues but sporadic in renal epithelial cells. In liver, omTERT mRNA was moderately expressed across the liver parenchyma except the red blood cells (Fig. 3V–X). omTERT and PCNA immunostaining were confined to the nucleus of hepatocytes. are consecutive tissue sections of those on the left, and were immunostained with anti-hTERT (mAb476) and anti-PCNA (M0879; DakoCytomation) monoclonal antibodies, respectively. Signal detection was accomplished with DAB (brown, positive signal). Sections were counterstained with hematoxylin (blue, negative signal). Testis (A–C): Sg, spermatogonia; Sc, spermatocyte; St, spermatid; Sz, spermatozoa. Ovary (D–F): PV, previtellogenic oocyte; cy, cytoplasm; n, nucleus; pn, provitelline nucleoli; VP, vitellogenic oocyte; yv, yolk vacuole; gc, granulose cell; af, attaching filament; tc, theca cell. Brain (G–I): Tel, telencephalon; OT, optic tectum; Ce, cerebellum; Rh, rhombencephalon; Hyp, hypothalamus. Skeletal muscle (J–L): MF, muscle fiber; n, nucleus. Gill (M-O): La, lamella; F, filament; CC, chloride cell; PC, pillar cell; MC, mucus cell; EC, epithelial cell; Ery, erythrocyte. Intestine (P–R): Lp, lamina propria; Me, mucosal epithelium; M, muscularis; Sm, serous membrane. Kidney (S–U): Gl, glomerulus; Rt, renal tubule; Lt, lymphoid tissue; Liver (V–X). Bars (A–C), (J–L) and (M–X) = 50 m; (D–F) = 100 m and (G–I) = 500 m. Author's personal copy 138 R.Y.C. Kong et al. / Aquatic Toxicology 86 (2008) 131–141 3.4. Relative expression levels of omTERT mRNA, omTERT protein and PCNA in different tissues of whole fish The magnitude of omTERT mRNA expression in different fish tissues was assessed by stereological analysis (expressed in volume density (Vv ) units) and was greatest in testes (which were full of dividing sperm cyst). In comparison, lower expression was observed in ovaries (containing few PV oocytes) while almost equivalent expression levels were detected among the regenerative organs (i.e., kidney, intestines, gill and liver). On the whole, expression of omTERT mRNA and protein, and PCNA was consistently higher in testes than in ovaries. The weakest omTERT mRNA level was observed in muscles (Fig. 4A). In general, the Vv value for omTERT protein is greater than the Vv value for omTERT mRNA in all tissues examined (Fig. 4B). Interestingly, the Vv value for PCNA was very similar to that of the omTERT protein in most fish tissues, except in liver and muscle where the PCNA Vv value was less (Fig. 4C). 3.5. Correlations Pearson’s correlation analyses showed a significant positive relationsip between omTERT mRNA and omTERT protein expression in male O. melastigma (r2 = 0.9104, p < 0.0001), however, the relationship was poor in female O. melastigma. There was also a statistically significant correlation between PCNA, with omTERT mRNA as well as omTERT protein for both male and female fish (Table 3). 3.6. Hypoxia O. melastigma were exposed to normoxia and hypoxia for 3 months. Fish mortality in the hypoxic group was 8% and mortality occurred mostly in the first 2 days of hypoxic exposure and no mortality was observable after 7 days. Adult male fish were processed for ISH and IHC. As shown in Fig. 5A, a significant induction of omTERT mRNA (p < 0.001) and a corresponding increase in omTERT protein (Fig. 5B; p < 0.01) was observed in liver hepatocytes of hypoxic male fish as compared Fig. 4. Volume density (Vv ) indices of (A) omTERT mRNA, (B) omTERT protein and (C) PCNA signals in different organs of male and female whole fish sections. Values represent the mean ± SEM; n = 5. Author's personal copy R.Y.C. Kong et al. / Aquatic Toxicology 86 (2008) 131–141 Table 3 Pearson correlation between (A) omTERT protein and omTERT mRNA, (B) PCNA and omTERT protein and (C) PCNA and omTERT mRNA expression (quantified by stereological volume density) in male and female adult O. melastigma (n = 5 fish × 6 organs) Coefficient of determination (r2 ) (A) omTERT mRNA vs. omTERT protein (B) PCNA vs. omTERT protein (C) PCNA vs. omTERT mRNA Male Female 0.9104*** 0.0159 0.8926*** 0.9233*** 0.1643* 0.3609*** Significant correlation is indicated by asterisks (* p < 0.05; *** p < 0.0001). to the normoxic control. Additionally, an increase in PCNApositive staining but reduced TUNEL (apoptotic) activity was also observed in the liver of hypoxic fish (Fig. 5C and D; p < 0.01). 4. Discussion The fixation and processing protocol developed for adult whole O. melastigma in this study is reproducible and costeffective for ISH and IHC analyses of the omTERT gene and protein, PCNA and TUNEL assay in multiple organs of a single fish. Applying these techniques to O. melastigma, we have demonstrated the feasibility of simultaneous expression and quantification analyses of multiple genes/proteins in whole fish sections without needing to dissect out individual organs for tissue processing, thereby facilitating high throughput molecular analyses in a small fish. Applying the ISH and IHC analyses on serial sections of O. melastigma, we further demonstrated that it is possible to simul- 139 taneously localize and correlate mRNA and protein expression in different fish tissues, as well as analyse the nucleocytoplasmic distribution of target protein molecules in specific cell types; which is not easily achievable by other molecular techniques. For instance, in previtellogenic oocytes, omTERT mRNA and protein were separately localised in the cytoplasm and nucleus, respectively (Fig. 3D and E), while in renal epithelial tubules and enterocytes of the intestinal mucosa, omTERT mRNA and protein were found in both the nuclear and cytosolic compartments. Alternatively, PCNA immuno-reactivity was confined largely to the nucleus of proliferative cells such as dividing sperm cells in testes, granulosa cells in ovarian follicles, neuronal cells in proliferative zones of the brain, epithelial cells of gill filaments, proliferative cells in the crypt region of mucosal folds and lymphoid tissues in kidneys. Although omTERT immunoreactivity was detected by IHC in fish ovary, kidney and intestines, Western blot analysis failed to detect any omTERT protein band of the expected size (ca.120 kDa) in either the nuclear or cytoplasmic fractions of these tissues. This could be due to low endogenous levels of the omTERT protein in these tissues that may be associated with factors such as batch variation (e.g. fewer PV oocytes in ovaries of female at late stages of oogenesis) or quality of protein extracts (e.g. contaminants in intestinal lumen). Nonetheless, the above findings indicate that IHC is a highly sensitive, reproducible and effective method for detection of omTERT protein in multiple tissues in vivo. Conceivably, the techniques developed in this study could be easily adapted to study in vivo expression of other genes and/or changes in cellular proteins in response to various stressors/toxicants in the marine environment. Stereological analysis of ISH signals as represented by volume density (Vv ) indices demonstrated similar patterns of Fig. 5. Volume density (Vv ) indices of (A) omTERT mRNA, (B) omTERT protein, (C) PCNA and (D) TUNEL signals in liver hepatocytes of male O. melastigma after chronic exposure to hypoxia (1.8 ± 0.2 mg O2 L−1 ) for 12 weeks. Values represent the mean ± SEM; n = 3 per treatment group. Values of hypoxia exposure groups that are significantly different from the normoxia controls (6.4 ± 0.2 mg O2 L−1 ) are indicated by asterisks (** p < 0.01, *** p < 0.001). Author's personal copy 140 R.Y.C. Kong et al. / Aquatic Toxicology 86 (2008) 131–141 omTERT mRNA distribution among organs of O. melastigma, relative to that measured by real-time RT-PCR in a previous study (Yu et al., 2006), whereby the level of gene expression was found to occur in the order: gonads regenerative tissues > livers, muscles. Likewise, quantification of the IHC results also revealed differential expression levels of the omTERT protein and PCNA in different organs of adult O. melastigma. Correlations between the Vv indices of omTERT mRNA and omTERT protein in O. melastigma tissues were statistically significant in male fish (r2 = 0.9104, p < 0.0001), but no correlation was observed in female fish, suggesting a sexspecific relationship between omTERT mRNA and protein in O. melastigma. This, however, should be further confirmed by studying more female individuals to allow correlation analysis at the organ level. The PCNA Vv indices were positively related to the omTERT mRNA and protein Vv indices in tissues of both male and female O. melastigma (Table 3), indicating that the possible involvement of omTERT expression in cell proliferation is not limited only to mammalian cancer cells in vitro (Greider, 1998; Smith et al., 2003), but is also pertinent for non-tumor fish cells in vivo. Our present findings show that whole adult O. melastigma provides a sensitive and versatile in vivo system for studying omTERT expression in multiple tissues/cells at different developmental and reproductive stages, which would help to provide further insights about the cellular role of TERT in growth, aging, reproduction and carcinogenesis, and its utility in environmental toxicology. A previous study using real-time RT-PCR (Yu et al., 2006) showed that exposure of O. melastigma to hypoxia for 96 h resulted in upregulated expression of omTERT mRNA in the fish liver. In the present study, using quantitative ISH (Vv index), we have also shown significant induction of omTERT mRNA in liver of male O. melastigma after a 12-week exposure to chronic hypoxia. This suggests that, unlike other hypoxiainducible genes (e.g. EPO and VEGF), in vivo expression of the omTERT gene in hypoxic livers of O. melastigma is a persistent, rather than a transient response. Induction of omTERT protein in the fish liver was accompanied by a concomitant and significant increase in PCNA and a reduction in TUNEL apoptotic activity. The PCNA and TUNEL results suggest a possible involvement of omTERT in the regulation of hepatocyte turnover in O. melastigma. It must be emphasized also that the same set of O. melastigma serial sections that were used for omTERT mRNA, omTERT protein, PCNA and TUNEL analyses in liver can be further quantified for similar molecular changes in other organs, and would therefore allow direct comparison of organ-specific molecular changes in response to hypoxic stress. In conclusion, the results of this study suggest that O. melastigma can potentially serve as a good marine fish model for ecotoxicological studies. The fixation and processing protocol we have developed for this whole fish system allows high throughput and concomitant in vivo quantification of a variety of target mRNA and proteins in different subcellular compartments and tissues in a single fish. This system confers significant advantages in studying in vivo molecular responses to a variety of toxicants/stresses in the marine environment. Acknowledgements This study was supported by a grant from the University Grants Committee of the Hong Kong Special Administrative Region, China (Project no. AoE/P-04/04) and CityU grants (Project nos. 7001834 and 7002117). The research was also supported, in part, by a grant from the US EPA STAR grant no. R-831846. The authors would like to thank Prof. Juro Koyama, Kagoshime University, Japan, for introducing us the O. melastigma. References Anken, R., Bourrat, F., 1998. Brain Atlas of the Medakafish. INRA ed., Paris. Au, D.W.T., 2004. 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