RESUMO
Cost-Effectiveness Analysis (CEA) is a decision-making framework to prioritize policy decisions for chemicals. Differences in hazard profiles among chemicals are not integrated in CEA under the EU REACH Regulation, which could limit its relevance. Another concern is that two different economic decision support methods (CEA for chemicals considered as PBTs or vPvBs from a regulatory perspective and Cost Benefit Analysis (CBA) for others) are used under REACH. To address this situation, we define "Hazard" CEA by integrating a hazard score, based on persistence, bioaccumulation and (eco)toxicity, in the effect indicator of CEA. We test different designs and parameterizations of Hazard-CEA on a set of past socio-economic assessments under REACH for PBT and non-PBT chemicals. Weighing and thresholds in hazard scores do not have a significant impact on the outcome of Hazard-CEA but the design of the hazard scoring method does. We suggest using an integrated and unweighted scoring method with a multiplicative formulation based on the notion of risk. Hazard-CEA could be used for both PBT and non-PBT chemicals, to use a single method in REACH and therefore improve consistency in policy decisions. Our work also suggests that using Hazard-CEA could help make decision easier.
Assuntos
Poluentes Ambientais , Substâncias Perigosas , Substâncias Perigosas/toxicidade , Substâncias Perigosas/análise , Poluentes Ambientais/análise , Análise de Custo-Efetividade , Monitoramento Ambiental/métodos , Gestão de Riscos , Análise Custo-BenefícioRESUMO
Several tons of chemicals are released every year into the environment and it is essential to assess the risk of adverse effects on human health and ecosystems. Risk assessment is expensive and time-consuming and only partial information is available for many compounds. A consolidated approach to overcome this limitation is the Threshold of Toxicological Concern (TTC) for assessment of the potential health impact and, more recently, eco-TTCs for the ecological aspect. The aim is to allow a safe assessment of substances with poor toxicological characterization. Only limited attempts have been made to integrate the human and ecological risk assessment procedures in a "One Health" perspective. We are proposing a strategy to define the Human-Biota TTCs (HB-TTCs) as concentrations of organic chemicals in freshwater preserving both humans and ecological receptors at the same time. Two sets of thresholds were derived: general HB-TTCs as preliminary screening levels for compounds with no eco- and toxicological information, and compound-specific HB-TTCs for chemicals with known hazard assessment, in terms of Predicted No effect Concentration (PNEC) values for freshwater ecosystems and acceptable doses for human health. The proposed strategy is based on freely available public data and tools to characterize and group chemicals according to their toxicological profiles. Five generic HB-TTCs were defined, based on the ecotoxicological profiles reflected by the Verhaar classes, and compound-specific thresholds for more than 400 organic chemicals with complete eco- and toxicological profiles. To complete the strategy, the use of in silico models is proposed to predict the required toxicological properties and suitable models already available on the VEGAHUB platform are listed.
Assuntos
Monitoramento Ambiental/métodos , Água Doce/química , Compostos Orgânicos , Medição de Risco , Poluentes Químicos da Água , Poluição Química da Água/prevenção & controle , Animais , Biota , HumanosRESUMO
Pharmaceuticals are emerging organic contaminants ubiquitously present in the environment due to incessant input into the aquatic compartment mainly resulting from incomplete removal in wastewater treatment plants. One of the major preoccupations concerning pharmaceuticals released into surface waters is their potential for bioaccumulation in biota, possibly leading to deleterious effects on ecosystems especially as they could affect a broad variety of organisms living in or depending on the aquatic environment. Thus, the development of accurate and sensitive methods is necessary to detect these compounds in aquatic ecosystems. Considering this need, this study deals with the analytical development of a methodology to quantify traces of diclofenac together with some of its biotic and abiotic transformation products in whole-body tissue of three-spined stickleback. A simple and reliable extraction method based on a modified QuEChERS extraction is implemented on 200 mg of fish. The detection and quantification of the ten target compounds are performed using liquid chromatography-tandem mass spectrometry. The whole process was successfully validated regarding linearity, recovery, repeatability, and reproducibility. The method limits of detection and quantification do not exceed 1 ng/g. To reproduce environmental conditions, we measured the concentration of DCF and its transformation products in three-spined sticklebacks after a 6-month exposure in mesocosms at several levels of DCF ranging from 0.05 to 4.1 µg/L. The phase I metabolite 4'-hydroxydiclofenac was detected in fish samples exposed at the highest DCF concentration. Graphical abstract Analysis of diclofenac and some of its transformation products in the three-spined stickleback, Gasterosteus aculeatus, by QuEChERS extraction followed by LC-MS/MS.
Assuntos
Cromatografia Líquida/métodos , Diclofenaco/química , Perciformes/metabolismo , Espectrometria de Massas em Tandem/métodos , Poluentes Químicos da Água/química , Animais , Diclofenaco/isolamento & purificação , Diclofenaco/metabolismo , Estrutura Molecular , Poluentes Químicos da Água/isolamento & purificação , Poluentes Químicos da Água/metabolismoRESUMO
Soils are a precious resource consistently placed under several threats and urgently in need of protection within a regulatory framework at the European level. Soils are central to the provision of environmental services as well as human existence on earth. The need to protect soil has been identified by several recent European strategies and fortunately, a specific European regulation for soil protection is on the way-the European Soil Monitoring Law (formerly: Soil Health Law). However, efforts need to ensure that the upcoming Soil Monitoring Law closes gaps between existing regulations for chemicals and acknowledges current European strategies for environmental protection and sustainability. This brief communication started from a fruitful discussion among SETAC Global Soils Interest Group members on a recent public consultation on the newly proposed Soil Monitoring Law of the European Commission and highlights critical points focusing on the chemical pollution of soils. We emphasize urgent needs such as the essential definition of a "healthy state" of soils; the implementation of a suitable set of indicators and quality standards for the description of physical, chemical, and biological states of soils; the enforcement of the "polluter-pays" principle; and the establishment of a Europe-wide monitoring program. Results from monitoring need to be fed back into regulatory frameworks, including the regulation of chemicals. Guidance documents for the risk assessment of chemicals are outdated and need to be updated. Finally, actions need to be taken to foster healthy soils, stop biodiversity decline, and ensure the functioning of ecosystem services for future generations. Integr Environ Assess Manag 2024;20:316-321. © 2023 The Authors. Integrated Environmental Assessment and Management published by Wiley Periodicals LLC on behalf of Society of Environmental Toxicology & Chemistry (SETAC).
Assuntos
Ecossistema , Solo , Humanos , Biodiversidade , Poluição Ambiental , Ecotoxicologia , Medição de Risco , Monitoramento Ambiental/métodosRESUMO
The aims of this work are to develop suitable analytical methods to determine the widely used anticonvulsant carbamazepine and 12 of its degradation/transformation products in water, sediment, fish (Gasterosteus aculeatus) and mollusc (Dreissena polymorpha). Protocols based on solid phase extraction for water, pressurized-liquid extraction for sediments and QuEChERS (quick easy cheap efficient rugged and safe) extraction for both organisms followed by liquid chromatography-tandem mass spectrometry (LC-MS/MS) are developed, validated and finally applied to samples collected during a 6-month experiment in outdoor mesocosms. Very low detection limits are reached, allowing environmentally realistic doses (namely, 0.05, 0.5 and 5 µg/L nominal concentrations) to be employed. The results indicate several metabolites and/or transformation products in each compartment investigated, with concentrations sometimes being greater than that of the parent carbamazepine. Biotic degradation of carbamazepine is demonstrated in water, leading to 10,11-dihydrocarbamazepine and 10,11-epoxycarbamazepine. In sediment, the degradation results in the formation of acridine, and 2- and 3-hydroxycarbamazepine. Finally, in both organisms, a moderate bioaccumulation is observed together with a metabolization leading to 10,11-epoxycarbamazepine in fish and 2-hydroxycarbamazepine in mollusc. Acridone is also present in fish. This study provides new and interesting data, helping to elucidate how chronic exposure to carbamazepine at relevant concentrations may affect impact freshwater ecosystems.
Assuntos
Carbamazepina/química , Poluentes Químicos da Água/química , Animais , Carbamazepina/análogos & derivados , Carbamazepina/análise , Cromatografia Líquida , Espectrometria de Massas em Tandem , Poluentes Químicos da Água/análiseRESUMO
Pharmaceuticals are ubiquitously present in the aquatic environment, mainly due to insufficient removal in wastewater treatment plants. Although these compounds are often found at trace levels in waters, long-term exposure can have negative impacts on biotic communities due to their inherent biological activity. The non-steroidal anti-inflammatory drug diclofenac (DCF) is one of the most frequently detected human pharmaceuticals in water and has recently been included in the "watch" list of the European Union. However little data are available on the detection of this substance and its transformation products in aquatic organisms. In this context, an analytical methodology has been developed to quantify traces of DCF along with its biotic and abiotic transformation products in a wild species of bivalve, the zebra mussel Dreissena polymorpha. A modified QuEChERS extraction was implemented on a small quantity of soft bivalve tissue (100mg). This was followed by liquid chromatography coupled to tandem-mass spectrometry (LC-MS/MS) with electrospray ionization in positive mode (ESI+). Whole analytical method was validated on spiked real samples, with regard to linearity (from 1 to 50 or 100ng/g depending on the target compounds, R(2)>0.99), intra-day precision (relative standard deviation (RSD)<18%), inter-day precision (RSD <25%), (recoveries 78-117%), and limits of detection and of quantification (both inferior or equal to 1ng/g). The optimized method was successfully applied to organisms collected from mesocosm experiments. Bioconcentration factors comprised between 4 and 13 were observed for DCF in the zebra mussels. To the best of our knowledge, the product 2-indolone was for the first time detected in bivalves, with levels up to 6ng/g.
Assuntos
Bivalves/metabolismo , Fracionamento Químico/métodos , Custos e Análise de Custo , Diclofenaco/isolamento & purificação , Diclofenaco/metabolismo , Ambiente Controlado , Segurança , Animais , Bivalves/química , Cromatografia Líquida , Diclofenaco/química , Monitoramento Ambiental , Reprodutibilidade dos Testes , Solventes/química , Espectrometria de Massas em TandemRESUMO
This paper details the results of perfusion experiments examining the accumulation of inorganic and methylmercury (Hg and MMHg) into the gill and intestine tissue of the blue crab, Callinectes sapidus. Additionally, the flux across the tissue to an internal medium, representative of crab tissue or haemolymph, during the perfusion was also measured. The accumulation and transfer processes were studied for each form by exposing the organs to a wide range of Hg and MMHg water concentrations, as well as a mixture of the two Hg forms. Experiments were also performed at different temperatures and in the presence of a metabolic inhibitor to assess the accumulation mechanisms. While the Hg levels bioaccumulated in the two organs were of the same order, the fluxes of Hg from the tissue to the internal medium were slightly higher in the intestine than in the gill. At low external concentrations, the uptake was very similar for both Hg forms, but as exposure pressure increased, inorganic Hg uptake slowed whereas MMHg uptake increased linearly. The results from the perfusion experiments with a mixture of inorganic Hg and MMHg show that while these two forms of Hg do share common uptake pathways, there is also independent uptake. The temperature and inhibition experiments with ouabain, a Na(+)K(+)ATPase inhibitor, show that accumulation is at least partially energy dependent. Overall, the results suggest that there is more than one mechanism of accumulation for both Hg forms. Finally, as accumulation of Hg and MMHg into these tissues was similar, these results contrast with the literature assertion that the enhanced bioaccumulation of MMHg over inorganic Hg is a result of MMHg being more readily transported across the gut membrane.
Assuntos
Braquiúros/metabolismo , Brânquias/metabolismo , Mercúrio/farmacocinética , Compostos de Metilmercúrio/farmacocinética , Poluentes Químicos da Água/farmacocinética , Animais , Técnicas de Cultura , Relação Dose-Resposta a Droga , Mucosa Intestinal/metabolismo , Perfusão , Temperatura , Distribuição TecidualRESUMO
An experimental study of the role of metallothioneins (MTs) in Cd and Zn depuration processes in the freshwater bivalve Corbicula fluminea was conducted after in situ exposure on the river Lot (France). Specimens of adult C. fluminea were first transplanted from a lacustrine reference site to a polymetallic polluted station (Bouillac, (B)) for a 42-days' exposure period from September to November 1996. They were then depurated after transfer to the laboratory, and were sub-sampled periodically until May 1997. During the first phase, MT concentrations measured with the Mercury-Saturation Assay were induced for a factor of 3.5 compared with time 0, whereas metal uptake showed accumulation factors of 17 and 4 for Cd and Zn, respectively. During the depuration phase, Cd and Zn concentrations decreased by 18 and 70%, respectively, giving estimated biological half-lives of 500 and 40 days. During the same period, MT concentrations decreased by 37% after transfer under unpolluted conditions, especially between 0 and 3 days, suggesting that MTs play a predominant role in Cd depuration. The quantity of Cd sequestered by the MT fraction, after size-exclusion liquid chromatography, represents on average 40% of the total Cd bioaccumulated in the soft body of the molluscs, compared with only 4-9% for total accumulated Zn. This essential metal was principally bound to low molecular weight proteins, which represented 20% of total Zn. Furthermore, it was observed that MTs had a key role in Cd remanence in the bivalves, and it was also reported that other proteins or small peptides were involved in the depuration of Zn.
Assuntos
Cádmio/efeitos adversos , Cádmio/farmacocinética , Metalotioneína/farmacologia , Moluscos/fisiologia , Poluentes da Água/efeitos adversos , Poluentes da Água/farmacocinética , Zinco/efeitos adversos , Zinco/farmacocinética , Animais , Cromatografia em Gel , Meia-Vida , Distribuição TecidualRESUMO
Using the perfusion method, we compared the accumulation and flux of inorganic mercury (Hg) and methylmercury (CH(3)Hg) across the gills and intestine of the blue crab, Callinectes sapidus. The accumulation and transfer processes were studied for each form by exposing the organs in the presence of specific ligands and other metals. While binding of Hg and CH(3)Hg to organic ligands reduced the rate of uptake in most instances, the differences in accumulation could not be explained only in terms of passive diffusive uptake. Thus, it appears that Hg and CH(3)Hg accumulation is dominated by ligand exchange or facilitated transport processes. Exposure of the gills and intestine in the presence of a suite of metals and metalloids showed that inorganic Hg and CH(3)Hg uptake was largely by different mechanisms to that of the other elements, as there was little interaction in terms of uptake rate. Overall, the results of this study suggest that inorganic Hg and CH(3)Hg uptake into the gills and intestine of this invertebrate is by a variety of pathways, both active and passive.