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1.
Aquat Toxicol ; 126: 242-55, 2013 Jan 15.
Article in English | MEDLINE | ID: mdl-23247545

ABSTRACT

Understanding the effects of chronic exposure to pollutants on the genome and transcriptome of diadromous fish populations is crucial for their resilience under combined anthropogenic and environmental selective pressures. The catadromous European eel (Anguilla anguilla L.) has suffered a dramatic decline in recruitment for three decades, necessitating a thorough assessment of the transcriptional effects of environmental pollutants on resident and migrating eels in natural systems. We investigated the relationship between muscular bioaccumulation levels of metals (Hg, Cd, Pb, Cu, Zn, Ni, Cr, As and Se), PCBs and organochlorine pesticides (DDTs), the health status (condition factor and lipid reserves) and the associated transcriptional response in liver and gill tissues for genes involved in metal detoxification (metallothionein, MT) and oxidative metabolism (cytochrome P4501A, CYP1A) of xenobiotic compounds. In total 84 resident eels originating from three Belgian river basins (Scheldt, Meuse and Yzer) were analyzed along with five unpolluted aquaculture samples as control group. There was a large spatial variation in individual contaminant intensity and profile, while tissue pollution levels were strongly and negatively associated with condition indices, suggesting an important impact of pollution on the health of sub-adult resident eels. Gene transcription patterns revealed a complex response mechanism to a cocktail of pollutants, with a high variation at low pollution levels, but strongly down-regulated hepatic and gill gene transcription in highly polluted eels. Resident eels clearly experience a high pollution burden and seem to show a dysfunctional gene transcription regulation of detoxification genes at higher pollutant levels, correlated with low energy reserves and condition. To fully understand the evolutionary implications of pollutants on eel reproductive fitness, analyses of mature migrating eels and the characterization of their transcriptome-wide gene transcription response would be appropriate to unveil the complex responses associated with multiple interacting stressors and the long-term consequences at the entire species level. In the meanwhile, jointly monitoring environmental and tissue pollution levels at a European scale should be initiated, while preserving high quality habitats to increase the recovery chance of European eel in the future.


Subject(s)
Anguilla , Environmental Exposure , Gene Expression Regulation/drug effects , Water Pollutants, Chemical/toxicity , Animals , Fish Proteins/genetics , Fresh Water/chemistry , Gene Expression Profiling , Health Status , Lipid A/analysis , Liver/chemistry , Liver/drug effects , Principal Component Analysis
2.
Chemosphere ; 86(10): 979-84, 2012 Mar.
Article in English | MEDLINE | ID: mdl-22154339

ABSTRACT

The organotin (OT) compounds tributyltin (TBT) and triphenyltin (TPhT) are potent biocides that have been used ubiquitously in antifouling paints and pesticides since the mid-1970s. These biocides are extremely toxic to marine life, particularly marine gastropod populations. The European Union therefore took measures to reduce the use of TBT-based antifouling paints on ships and ultimately banned these paints in 2003. Despite sufficient data on OT concentrations in marine gastropods, data are scarce for other species such as the North Sea brown shrimp (Crangon crangon), a dominant crustacean species in North Sea inshore benthic communities. The present study provides the first spatial overview of OT concentrations in North Sea brown shrimp. We have compared these data with historical concentrations in shrimp as well as with sediment concentrations. We have also addressed the effect on the shrimp stock and any human health risks associated with the OT concentrations found. TBT and TPhT in shrimp tail muscle ranged from 4 to 124 and from 1 to 24 µg kg(-1) DW, respectively. High levels are accumulated in estuarine areas and are clearly related with sediment concentrations (biota-sediment accumulation factor ~10). Levels have decreased approximately 10-fold since the ban took effect, coinciding with a recovery of the shrimp stock after 30 years of gradual regression. Furthermore, the OT levels found in brown shrimp no longer present a human health risk.


Subject(s)
Crangonidae/metabolism , Organotin Compounds/metabolism , Water Pollutants, Chemical/metabolism , Water Pollution, Chemical/statistics & numerical data , Animals , Diet/statistics & numerical data , Environmental Monitoring , Geologic Sediments/chemistry , Humans , Legislation as Topic , Organotin Compounds/analysis , Risk Assessment , Trialkyltin Compounds/analysis , Trialkyltin Compounds/metabolism , Water Pollutants, Chemical/analysis , Water Pollution, Chemical/legislation & jurisprudence
3.
Food Addit Contam ; 17(9): 755-62, 2000 Sep.
Article in English | MEDLINE | ID: mdl-11091788

ABSTRACT

The obvious toxicity of cadmium and lead is at the basis of compulsory concentration determinations for lixiviation solutions of ceramic and earthenware household receptacles such as cups, plates, bowls and others. Concentrations in the food simulant which exceed 0.100 +/- 0.005 mg Cd dm-2 and 1.00 +/- 0.05 mg Pb dm-2 for flat receptacles, 0.500 +/- 0.025 mg Cd l-1 and 5.00 +/- 0.25 mg Pb l-1 for low volume (< 5 l) receptacles and 0.250 +/- 0.025 mg Cd l-1 and 2.50 +/- 0.25 mg Pb l-1 for high volume (> 5 l) receptacles are not acceptable and measures were taken by the EU member state authorities to enforce these norm concentrations. Generally, the uncertainty on the results forwarded by the legislation amounts to 5%. This value does not at all match the pronounced variability observed for several 'identical' trade samples, but rather represents the inherent variability of spectrometric analyses alone. Considering that the coefficients of variation can be as high as approximately 30%, either the ranges of acceptable concentrations or the maximal allowable concentrations should be corrected. Aware of the negative health effects of heavy metal contamination and of the risk increase due to dietary intake, a downward adjustment of the acceptable concentration ranges to 0.07 mg Cd dm-2 +/- 12%, 0.30 mg Cd l-1 +/- 12% and 0.10 mg Cd l-1 +/- 12% and to 0.8 mg Pb dm-2 +/- 13%, 4.0 mg Pb l-1 +/- 13% and 1.50 mg Pb l-1 +/- 13% is suggested.


Subject(s)
Cadmium/analysis , Cooking and Eating Utensils , Food Contamination/analysis , Lead/analysis , Maximum Allowable Concentration , Reference Values , Reproducibility of Results , Spectrophotometry, Atomic
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