No abstract

No abstract

No abstract

No abstract

No abstract

No abstract

To establish a monitoring system for gene expression profiles related to chemical contamination in wild common cormorants (Phalacrocorax carbo), the present study constructed an oligo array designed from expressed sequence tag (EST) sequences of the cormorant liver, where 1061 unique oligonucleotides were spotted. Common cormorants were collected from Lake Biwa, Japan in May 2001 and 2002. With the use of this oligo array, gene expression profiles in the liver of individual specimens were evaluated. To determine the expression patterns of genes altered by environmental contaminants, relationships between concentrations of persistent organochlorines including polychlorinated dibenzo-p-dioxins, furans, polychlorinated biphenyls, 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane and its metabolites (DDTs), hexachlorocyclohexane isomers (HCHs), chlordane compounds (CHLs), butyltins, and bisphenol A (BPA) and expression levels of each gene in the cormorant liver were examined using stepwise multiple regression analysis. The reliability of data obtained by the oligo array was further confirmed by quantifying the expression levels of certain genes using real-time RT-PCR. The 2,3,7,8-tetrachlorodibenzo-p-dioxin toxic equivalent (TEQ) level was positively correlated with both cytochrome P4501A4 and 1A5 gene expression. In addition, the mRNA level of an antioxidant enzyme, Cu/Zn superoxide dismutase, was negatively correlated with hepatic total TEQ. Other antioxidant enzymes, glutathione peroxidase 3 and glutathione S-transferase class mu, were negatively correlated with HCHs and BPA levels, respectively. The mRNA expression level of a nonenzymatic antioxidant, haptoglobin, was negatively but not significantly correlated with CHLs. These results led to a hypothesis that wild cormorant population may suffer from oxidative stress due to chemically induced formation of reactive oxygen species and subsequent reduction of antioxidant resistance. Thus, the cormorant oligo array may be a useful monitoring tool to identify specific gene expression profiles altered by various environmental contaminants. Although further research is required to clarify a definitive cause-and-effect relationship, the current study provides valuable information on contaminant-responsive genes to predict potential effects on wildlife in a real environment.

The effects of polychlorinated biphenyls (PCBs; Kanechlor 400) on the schooling behavior of Japanese medaka (Oryzias latipes) were tested after feeding with various concentrations of PCBs (0, 1, 5, 25, and 125 microg/g). To test schooling, three PCB-exposed medaka and three untreated fish were placed in one chamber, and their swimming trajectories were recorded. Swimming velocity, turning angle, and nearest-neighbor distance (NND) were analyzed individually, and the polarization and expanse of each schooling group were analyzed. Fractal dimension analysis was performed for trajectory, swimming velocity, and turning angle. Six behaviors (school formed by six swimming medaka, school formed by six stationary medaka, school formed by three to five swimming medaka, school formed by three to five stationary medaka, swimming without schooling, and stationary without schooling) were quantified with time. Behavioral parameters were the same for PCB-exposed and unexposed medaka in the same schooling group. Swimming velocity decreased in a dose-dependent manner, and NND in the group exposed to 25 microg/g of PCBs was significantly longer (126%) than that in the controls. The fractal dimensions of trajectory and turning angle increased significantly in the highest PCB-exposure group, indicating that schools containing PCB-exposed individuals frequently changed direction. The PCBs shortened the time of school formed by six swimming fish, which was 23.7% of the control value in the group exposed to 25 microg/g of PCBs. The frequency of collisions between individuals was significantly greater in the highest-exposure group (31.3) than in the controls (13.3). Thus, PCB exposure influences the behavior of unexposed fish in the same school, consequently affecting schooling behavior.