Построение многомерного распределения доходностей с использованием копула-функций

Perfluorooctane sulfonate (PFOS; C8F17SO3–) is a fully fluorinated organic compound which has been manufactured for decades and was used widely in industrial and commercial products. The recent toxicological knowledge of PFOS mainly concerns mono-substance exposures of PFOS to biological systems, leaving the potential interactive effects of PFOS with other compounds as an area where understanding is significantly lacking. However, a recent study, reported the potential of PFOS to enhance the toxicity of two compounds by increasing cell membrane permeability. This is of particular concern since PFOS has been reported to be widely distributed in the environment where contaminants are known to occur in complex mixtures. In this study, PFOS was evaluated alone and in combination with cyclophosphamide (CPP) to investigate whether a presence of PFOS leads to an increased genotoxic potential of CPP towards hamster lung V79 cells. Genotoxicity was investigated using the micronucleus(MN) assay according to the recent draft ISO/DIS 21427-2 method. PFOS alone demonstrated no genotoxicity up to a concentration of 12.5 μg/ml. However, PFOS combined with two different concentrations of CPP, with metabolic activation, caused a significant increase in the number of micronucleated cells compared to treatments with CPP alone. These results provide a first indication that PFOS has the potential to enhance the genotoxic action of CPP towards V79 cells, suggesting, together with the alterations in cell membrane properties shown previously, that genotoxicity of complex mixtures may be increased significantly by changes in chemical uptake. Together with an earlier study performed by the own working group, it can be concluded that PFOS alone is not genotoxic in this bioassay using V79 cells up to 12.5 μg/ml, but that further investigations are needed to assess the potential interaction between PFOS and other substances, in particular regarding the impact of membrane alterations on the uptake of toxic substances.</p

Occurrence and temporal variations of TMDD in the river Rhine, Germany

Background, aim, and scope: The chemical substance 2,4,7,9-tetramethyl-5-decyne-4,7-diol (TMDD) is a non-ionic surfactant used as an industrial defoaming agent and in various other applications. Its commercial name is Surynol 104® and the related ethoxylates are also available as Surfynol® 420, 440, 465 and 485 which are characterized by different grades of ethoxylation of TMDD at both hydroxyl functional groups. TMDD and its ethoxylates offer several advantages in waterborne industrial applications in coatings, inks, adhesives as well as in paper industries. TMDD and its ethoxylates can be expected to reach the aquatic environment due its widespread use and its physico-chemical properties. TMDD has previously been detected in several rivers of Germany with concentrations up to 2.5 µg/L. In the United States, TMDD was also detected in drinking water. However, detailed studies about its presence and distribution in the aquatic environment have not been carried out so far. The aim of the present study was the analysis of the spatial and temporal concentration variations of TMDD in the river Rhine at the Rheingütestation Worms (443.3 km). Moreover, the transported load in the Rhine was investigated during two entire days and 7 weeks between November 2007 and January 2008. Materials and methods: The sampling was carried out at three different sampling points across the river. Sampling point MWL1 is located in the left part of the river, MWL2 in the middle part, and MWL4 in the right part. One more sampling site (MWL3) was run by the monitoring station until the end of 2006, but was put out of service due to financial constrains. The water at the left side of the river Rhine (MWL1) is influenced by sewage from a big chemical plant in Ludwigshafen and by the sewage water from this city. The water at the right side of the river Rhine (MWL4) is largely composed of the water inflow from river Neckar, discharging into Rhine 14.9 km upstream from the sampling point and of communal and industrial wastewater from the city Mannheim. The water from the middle of the river (MWL2) is largely composed of water from the upper Rhine. Water samples were collected in 1-L bottles by an automatic sampler. The water samples were concentrated by use of solid-phase extraction (SPE) using Bond Elut PPL cartridges and quantified by use of gas chromatography-mass spectrometry (GC-MS). The quantification was carried out with the internal standard method. Based on these results, concentration variations were determined for the day profiles and week profiles. The total number of analyzed samples was 219. Results: The results of this study provide information on the temporal concentration variability of TMDD in river Rhine in a cross section at one particular sampling point (443.3 km). TMDD was detected in all analyzed water samples at high concentrations. The mean concentrations during the 2 days were 314 ng/L in MWL1, 246 ng/L in MWL2, and 286 ng/L in MWL4. The variation of concentrations was low in the day profiles. In the week profiles, a trend of increasing TMDD concentrations was detected particularly in January 2008, when TMDD concentrations reached values up to 1,330 ng/L in MWL1. The mean TMDD concentrations during the week profiles were 540 ng/L in MWL1, 484 ng/L in MWL2, and 576 ng/L in MWL4. The loads of TMDD were also determined and revealed to be comparable in all three sections of the river. The chemical plant located at the left side of the Rhine is not contributing additional TMDD to the river. The load of TMDD has been determined to be 62.8 kg/d on average during the entire period. By extrapolation of data obtained from seven week profiles the annual load was calculated to 23 t/a. Discussion: The permanent high TMDD concentrations during the investigation period indicate an almost constant discharge of TMDD into the river. This observation argues for effluents of municipal wastewater treatment plants as the most likely source of TMDD in the river. Another possible source might be the degradation of ethoxylates of TMDD (Surfynol® series 400), in the WWTPs under formation of TMDD followed by discharge into the river. TMDD has to be considered as a high-production-volume (HPV) chemical based on the high concentrations found in this study. In the United States, TMDD is already in the list of HPV chemicals from the Environmental Protection Agency (EPA). However, the amount of TMDD production in Europe is unknown so far and also the biodegradation rates of TMDD in WWTPs have not been investigated. Conclusions: TMDD was found in high concentrations during the entire sampling period in the Rhine river at the three sampling points. During the sampling period, TMDD concentrations remained constant in each part of the river. These results show that TMDD is uniformly distributed in the water collected at three sampling points located across the river. ‘Waves’ of exceptionally high concentrations of TMDD could not be detected during the sampling period. These results indicate that the effluents of WWTPs have to be considered as the most important sources of TMDD in river Rhine. Recommendations and perspectives: Based also on the occurrence of TMDD in different surface waters of Germany with concentrations up to 2,500 ng/L and its presence in drinking water in the USA, more detailed investigations regarding its sources and distribution in the aquatic environment are required. Moreover, the knowledge with respect to its ecotoxicity and its biodegradation pathway is scarce and has to be gained in more detail. Further research is necessary to investigate the rate of elimination of TMDD in municipal and industrial wastewater treatment plants in order to clarify the degradation rate of TMDD and to determine to which extent effluents of WWTPs contribute to the input of TMDD into surface waters. Supplementary studies are needed to clarify whether the ethoxylates of TMDD (known as Surfynol 400® series) are hydrolyzed in the aquatic environment resulting in formation of TMDD similar to the well known cleavage of nonylphenol ethoxylates into nonylphenols. The stability of TMDD under anaerobic conditions in groundwater is also unknown and should be studied

Long-term effects of a binary mixture of perfluorooctane sulfonate (PFOS) and bisphenol A (BPA) in zebrafish

The frequent use of perfluorinated chemicals (PFCs) in industrial applications and domestic products has led on a global basis to a continuous detection of PFCs in a wide range of environmental matrices including aquatic systems. Perfluorooctane sulfonate (PFOS) is the most commonly detected PFC in biotic and abiotic samples. To date, the understanding of the potential effects of PFOS towards biological systems has reached substantial progress. However, the majority of studies have focused on acute effects, leaving long-term effects largely unexplored. Given the persistent properties and the reported membrane altering potential of PFOS a long-term assessment in combination with other pollutants should be a promising strategy to shed more light on the complex toxicology of PFOS. Since PFOS has been shown to act as an endocrine disruptorin fish a combined investigation with another endocrine disrupting chemical (EDC) would represent an approach where specific endpoints such as sex steroid levels could be measured and compared, thus providing a more direct hint of any interactive effects. In the present study we investigated waterborne PFOS both alone and in a binary mixture with the known EDC bisphenol A (BPA) over two full generations of the zebrafish (Danio rerio). Survival, growth, reproductive success, vitellogenin (VTG) and histological alterations in thyroid, liver and gonads were examined. PFOS (300 μg/L) was found to induce lipid accumulation in liver of F1 generation fish. A parallel finding in PFOS (300 μg/L) exposed fish was the occurrence of granuloma, presumably as a result of bacterial infection. Identical granuloma structures were detected in lower PFOS concentrations in F2 generation fish, indicating a suppressed immune system over generations. BPA tended to increase plasma VTG concentrations whereas the opposite trend was observed for PFOS. Binary mixtures of the two chemicals indicated no synergisticeffects. Conclusively our study does not validate the hypothesis that the presence of PFOS increases the endocrine potential of BPA. However, our results indicate an immune suppressing potential of PFOS which seems to be enhanced over generations

Long-term effects of a binary mixture of perfluorooctane sulfonate (PFOS) and bisphenol A (BPA) in zebrafish

The frequent use of perfluorinated chemicals (PFCs) in industrial applications and domestic products has led on a global basis to a continuous detection of PFCs in a wide range of environmental matrices including aquatic systems. Perfluorooctane sulfonate (PFOS) is the most commonly detected PFC in biotic and abiotic samples. To date, the understanding of the potential effects of PFOS towards biological systems has reached substantial progress. However, the majority of studies have focused on acute effects, leaving long-term effects largely unexplored. Given the persistent properties and the reported membrane altering potential of PFOS a long-term assessment in combination with other pollutants should be a promising strategy to shed more light on the complex toxicology of PFOS. Since PFOS has been shown to act as an endocrine disruptorin fish a combined investigation with another endocrine disrupting chemical (EDC) would represent an approach where specific endpoints such as sex steroid levels could be measured and compared, thus providing a more direct hint of any interactive effects. In the present study we investigated waterborne PFOS both alone and in a binary mixture with the known EDC bisphenol A (BPA) over two full generations of the zebrafish (Danio rerio). Survival, growth, reproductive success, vitellogenin (VTG) and histological alterations in thyroid, liver and gonads were examined. PFOS (300 μg/L) was found to induce lipid accumulation in liver of F1 generation fish. A parallel finding in PFOS (300 μg/L) exposed fish was the occurrence of granuloma, presumably as a result of bacterial infection. Identical granuloma structures were detected in lower PFOS concentrations in F2 generation fish, indicating a suppressed immune system over generations. BPA tended to increase plasma VTG concentrations whereas the opposite trend was observed for PFOS. Binary mixtures of the two chemicals indicated no synergisticeffects. Conclusively our study does not validate the hypothesis that the presence of PFOS increases the endocrine potential of BPA. However, our results indicate an immune suppressing potential of PFOS which seems to be enhanced over generations

Long-term effects of a binary mixture of perfluorooctane sulfonate (PFOS) and bisphenol A (BPA) in zebrafish (Danio rerio).

Previous in vitro studies have reported the potential of perfluorooctane sulfonate (PFOS) to increase the toxicity of other compounds. Given the complex nature of mixtures of environmental pollutants in aquatic systems together with the persistent and bioaccumulative properties of PFOS, this study aimed at evaluating the long-term effects and toxicity-increasing behavior of PFOS in vivo using the zebrafish (Danio rerio). Fish were maintained in flow-through conditions and exposed to single and binary mixtures of PFOS and the endocrine disruptor bisphenol A (BPA) at nominal concentrations of 0.6, 100 and 300 mu g/L and 10, 200 and 400 mu g/L, respectively. F1 and F2 generations were evaluated from 0 to 180 days post-fertilization (dpf) and F3 generation was evaluated from 0 to 14 dpf. Survival was documented in all generations, whereas growth, fecundity, fertilization rate, histological alterations (in liver, thyroid and gonads) and vitellogenin (Vtg) induction in males were evaluated for Fl and F2 generations. Data for growth were collected at 30, 90 and 180 dpf and data for histological evaluations and Vtg induction were analyzed at 90 and 180 dpf. No significant effects on survival were seen in the Fl generation in any treatment following 180 d exposure: however, in the F2 generation, 300 mu g/L PFOS both alone and in combination with BPA (10, 200 and 400 mu g/L) induced 100% mortality within 14 dpf. PFOS (0.6 and 300 mu g/L) did not increase the Vtg-inducing potential of BPA (10, 200 and 400 mu g/L) in a binary mixture. In contrast, binary mixtures with 300 mu g/L PFOS suppressed the Vtg levels in Fl males at 90 dpf when compared to single BPA exposures. Whereas the lowest tested PFOS concentration (0.6 mu g/L) showed an estrogenic potential in terms of significant Vtg induction, Vtg levels were generally found to decrease with increasing PFOS-exposure in both Fl and F2 generations. In Fl generation, BPA-exposure was found to increase Vtg levels in a concentration-dependent manner. Histological analyses of Fl and F2 fish revealed hepatocellular vacuolization, predominantly in males, following PFOS-exposure both alone and in combination with BPA. Hepatotoxicity by PFOS might explain the suppressed Vtg response seen in PFOS-exposed Fl and F2 males. PFOS-exposed fish also showed granulomas, mainly in the liver. Given previous reports of the immunosuppressive potential of PFOS, the granulomas could be a consequence of a PFOS-induced reduction of the immune response potential. In conclusion, the hypothesis that the presence of PFOS increases the endocrine potential of BPA could not be confirmed in zebrafish. Adverse effects on liver structure and survival were only seen at concentrations well above ecologically relevant concentrations; however, the decline in survival rates following PFOS-exposure seen over generations again documents the importance of long-term studies for the investigation of persistent environmental pollutants.</p