RESUMEN
Marine mammals in the past mass mortality events may have been susceptible to infection because their immune systems were suppressed through the bioaccumulation of environmental pollutants such as polychlorinated biphenyls (PCBs). We compiled mortality event data sets of 33 marine mammal species, and employed a Finely-Advanced Transboundary Environmental model (FATE) to model the exposure of the global fish community to PCB congeners, in order to define critical exposure levels (CELs) of PCBs above which mass mortality events are likely to occur. Our modelling approach enabled us to describe the mass mortality events in the context of exposure of higher-trophic consumers to PCBs and to identify marine pollution 'hotspots' such as the Mediterranean Sea and north-western European coasts. We demonstrated that the CELs can be applied to quantify a chemical pollution Planetary Boundary, under which a safe operating space for marine mammals and humanity can exist.
Asunto(s)
Mamíferos , Modelos Teóricos , Mortalidad , Bifenilos Policlorados/toxicidad , Contaminantes Químicos del Agua/toxicidad , Animales , Organismos Acuáticos , Monitoreo del Ambiente , Contaminantes Ambientales , Contaminación Ambiental , Femenino , Cadena Alimentaria , Masculino , Mar Mediterráneo , Océanos y MaresRESUMEN
Spills of heavy oil (HO) have an adverse effect on marine life. We have demonstrated previously that exposure to HO by fertilized eggs of the pufferfish (Takifugu rubripes) induces neural disruption and behavioral abnormality in early-hatched larvae. Here, two kinds of polycyclic aromatic hydrocarbons, pyrene and phenanthrene, were selected to examine their toxic effects on larval behavior of another pufferfish species (T. niphobles). Larvae exposed to pyrene or phenanthrene exhibited no abnormalities in morphology. However, those exposed to pyrene but not phenanthrene swam in an uncoordinated manner, although their swimming distance and speed were normal. The optic tectum, a part of the midbrain, of pyrene-exposed larvae did not grow to full size. Thus, these findings are indicated that pyrene might be a contributor to the behavioral and neuro-developmental toxicity, although there is no indication that it is the only compound participating in the toxicity of the heavy oil mixture.
Asunto(s)
Conducta Animal/efectos de los fármacos , Fenantrenos/toxicidad , Pirenos/toxicidad , Natación , Tetraodontiformes/fisiología , Animales , Larva/efectos de los fármacos , Larva/fisiología , Mesencéfalo/anatomía & histología , Mesencéfalo/efectos de los fármacos , Tamaño de los Órganos/efectos de los fármacosRESUMEN
We propose a new metric for long-range transport potential (LRTP), GIF, based on source-receptor analyses and evaluate the LRTP and persistence of a wide variety of chlorinated and brominated organic compounds using GIF and overall persistence (POV), respectively. We calculated GIF and POV using our global 3D dynamic multimedia model (FATE). Physicochemical properties were obtained from quantitative structure-property relationship (QSPR) models. The FATE-QSPR combined model enabled us to systematically investigate the LRTP and persistence of a wide variety of chemical substances. On average, the estimated GIF and POV for chlorinated compounds were larger than those for their brominated counterparts, with the largest and smallest values found for polychlorinated biphenyls and polybrominated dibenzodioxins, respectively. We also compared GIF with four differently defined LRTP metrics and two LRTP metrics obtained from a simple model. The results of our analyses indicate that the LRTP ranks can differ considerably among LRTP metrics, the differences being dependent on the governing environmental processes, relevant physicochemical properties, and multimedia model.
Asunto(s)
Monitoreo del Ambiente/métodos , Contaminantes Ambientales/análisis , Contaminación Ambiental/análisis , Hidrocarburos Halogenados/análisis , Modelos Teóricos , Relación Estructura-Actividad CuantitativaRESUMEN
The effects of polychlorinated biphenyls (PCBs) on liver function and their differences between sexes were analyzed in Japanese medaka (Oryzias latipes) exposed to PCB126 or Kanechlor-400 (KC-400) using microarray. PCB exposure induced vitellogenin 1 expression in female medaka while suppressing choriogenin genes, which suggests that the effects of PCBs on estrogen-responsive genes do not occur directly through an estrogen receptor-mediated pathway. Reduction of androgen receptor alpha expression was also observed, and the gene expression pattern in PCB-exposed males changed to become more similar to that of females. Furthermore, changes in glycolysis-related genes indicate that PCB exposure might enhance glucose production via gluconeogenesis in the liver of medaka. Taken together, our results suggest that PCBs disrupt the endocrine system, especially androgen function, and may have the potential to cause demasculinizing effects. Additionally, induction of gluconeogenesis might be a response to maintain glucose levels consumed as a result of PCB exposures.
Asunto(s)
Trastornos del Desarrollo Sexual/inducido químicamente , Disruptores Endocrinos/toxicidad , Hígado/efectos de los fármacos , Bifenilos Policlorados/toxicidad , Caracteres Sexuales , Contaminantes Químicos del Agua/toxicidad , Animales , Trastornos del Desarrollo Sexual/metabolismo , Femenino , Proteínas de Peces/genética , Proteínas de Peces/metabolismo , Hígado/metabolismo , Hígado/patología , Masculino , Oryzias , Factores Sexuales , Vitelogeninas/genética , Vitelogeninas/metabolismoRESUMEN
BACKGROUND AND OBJECTIVE: Spills of heavy oil (HO) over the oceans have been proven to have an adverse effect on marine life. It has been hypothesized that exposure of early larvae of sinking eggs to HO leads largely to normal morphology, whereas abnormal organization of the developing neural scaffold is likely to be found. HO-induced disruption of the nervous system, which controls animal behavior, may in turn cause abnormalities in the swimming behavior of hatched larvae. To clarify the toxicological effects of HO, we performed exposure experiments and morphological and behavioral analyses in pufferfish (Takifugu rubripes) larvae. EXPERIMENTAL PROCEDURE: Fertilized eggs of pufferfish were exposed to 50 mg/L of HO for 8 days and transferred to fresh seawater before hatching. The hatched larvae were observed for their swimming behavior, morphological appearance, and construction of muscles and nervous system. RESULTS AND DISCUSSION: In HO-exposed larvae, we did not detect any anomaly of body morphology. However, they showed an abnormal swimming pattern and disorganized midbrain, a higher center controlling movement. Our results suggest that HO-exposed fishes suffer developmental disorder of the brain that triggers an abnormal swimming behavior and that HO may be selectively toxic to the brain and cause physical disability throughout the life span of these fishes.
Asunto(s)
Conducta Animal/efectos de los fármacos , Enfermedades del Sistema Nervioso Central/veterinaria , Enfermedades de los Peces/inducido químicamente , Petróleo/toxicidad , Tetraodontiformes , Contaminantes Químicos del Agua/toxicidad , Animales , Enfermedades del Sistema Nervioso Central/inducido químicamente , Enfermedades del Sistema Nervioso Central/patología , Enfermedades de los Peces/patología , Natación , Factores de TiempoRESUMEN
Here we propose a novel microarray data analysis method applicable to evaluation of the chemical effects on wild animals. First, we analyzed correlations between log-transformed hepatic 2,3,7,8-tetrachlorodibenzo-p-dioxin toxic equivalent (TEQ) levels and probe signals detected in wild cormorant liver to screen contaminant-responsive genes. Second, principal component analysis (PCA) was conducted using the screened probes. Third, these probes were divided into two groups based on our PCA result. Finally, we calculated Euclidian distance of signals, which is equivalent to variance of gene expressions, in each probe set, and analyzed the relationship between log-transformed hepatic TEQ levels and Euclidian distances. A probe set whereby the calculated Euclidian distance was positively correlated with TEQ levels, could indicate genes that were directly affected by dioxins or other persistent organic pollutants (POPs), hence they can be used as biomarkers. By contrast, there were a number of probes whereby the Euclidian distance was negatively correlated with TEQ levels. In the latter probe group, the smaller Euclidian distances in highly contaminated individuals could point to changes in physiological activities of wild cormorants. Therefore, our microarray data analysis method will provide new insights into POPs-responsive genes in field-collected samples for toxicogenomics studies.
Asunto(s)
Aves/metabolismo , Monitoreo del Ambiente/métodos , Contaminantes Ambientales/toxicidad , Perfilación de la Expresión Génica/métodos , Análisis de Secuencia por Matrices de Oligonucleótidos/métodos , Dibenzodioxinas Policloradas/toxicidad , Animales , Aves/genética , Expresión Génica/efectos de los fármacos , Hígado/metabolismoRESUMEN
Phytoplankton play a vital role in determining the fate and transport of persistent organic pollutants (POPs) in aquatic ecosystems. Lipids in phytoplankton cells can accumulate POPs, and equilibrium partitioning of the chemicals between lipids and water can be deduced from the octanol/water partition coefficient (K(ow)). However, there is much uncertainty in the response of the bioconcentration factor (BCF) to K(ow). While distinct level-off and bell-shaped responses of BCF to K(ow) have been confirmed by laboratory experiments, a mathematical basis for the non-linear processes has been lacking. Using two differential equation models (Water-Phytoplankton and Water-Phytoplankton-Dissolved Organic Carbon) we here examine previously reported non-linearity between BCF and K(ow). Our modelling studies suggest that a level-off response of the true BCF (BCF estimated at equilibrium) to K(ow) could be attributed to the presence of dissolved organic carbon (DOC). The alternative bell-shaped response appears to be a consequence of the apparent BCF (BCF estimated at non-equilibrium) for which the slow uptake rate of chemical compounds of relatively large molecular mass by phytoplankton is responsible.