25 research outputs found

    Uptake and depuration of gold nanoparticles in Daphnia magna

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    This study presents a series of short-term studies (total duration 48 h) of uptake and depuration of engineered nanoparticles (ENP) in neonate Daphnia magna. Gold nanoparticles (Au NP) were used to study the influence of size, stabilizing agent and feeding on uptake and depuration kinetics and animal body burdens. 10 and 30 nm Au NP with different stabilizing agents [citrate (CIT) and mercaptoundecanoic acid (MUDA)] were tested in concentrations around 0.5 mg Au/L. Fast initial uptake was observed for all studied Au NP, with CIT stabilized Au NP showing similar rates independent of size and MUDA showing increased uptake for the smaller Au NP (MUDA 10 nm > CIT 10 nm, 30 nm > MUDA 30 nm). However, upon transfer to clean media no clear trend on depuration rates was found in terms of stabilizing agent or size. Independent of stabilizing agent, 10 nm Au NP resulted in higher residual whole-animal body burdens after 24 h depuration than 30 nm Au NP with residual body burdens about one order of magnitude higher of animals exposed to 10 nm Au NP. The presence of food (P. subcapitata) did not significantly affect the body burden after 24 h of exposure, but depuration was increased. While food addition is not necessary to ensure D. magna survival in the presented short-term test design, the influence of food on uptake and depuration kinetics is essential to consider in long term studies of ENP where food addition is necessary. This study demonstrates the feasibility of a short-term test design to assess the uptake and depuration of ENP in D. magna. The findings underlines that the assumptions behind the traditional way of quantifying bioconcentration are not fulfilled when ENPs are studied.Peer reviewed: YesNRC publication: Ye

    An assessment of the importance of exposure routes to the uptake and internal localisation of fluorescent nanoparticles in zebrafish (Danio rerio), using light sheet microscopy

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    According to the United Nations, plastic pollution in the natural environment has been identified as one of the biggest environmental challenges of this century and has become a cause for an emerging international concern. It has been predicted that up to 12 million tons of plastic waste reach the aquatic environment annually. Therein, UV-radiation induced photo-oxidation, mechanical weathering and biological degradation contribute to the fragmentation of plastic litter to the micro- or even nanoscale. Microplastics (MPs) thus have become prominent pollutants in the aquatic environment, and their prevalence has been documented in every aquatic ecosystem studied. MPs enter aquatic food webs, also reaching humans, the top consumers in the food chain. The omnipresence of small microscopic plastic particles in the aquatic environment presents several ecotoxicological concerns. Firstly, MP fragments can interact with aquatic organisms and act as physical or mechanical stressors. Secondly, MPs can be toxic, as some polymers consist of potentially hazardous monomers. Synthetic, petroleum-derived polymers can also contain functional additives, impurities or chemical residuals, which are not chemically bound to the polymeric material and thus have the potential to leach out and cause diverse toxicological effects. Lastly, plastic polymers are known to absorb persistent hydrophobic organic pollutants from the environment. MPs have been suggested to act as vectors of environmental contaminants into organisms, promote bioaccumulation of toxic compounds, and cause biological effects in aquatic biota. It remains widely debated whether MPs are important vectors of chemicals for aquatic animals, including fish, and whether MP ingestion by edible fish species can impact human food quality and safety. This PhD project addressed some of these prevailing concerns, and investigated biological fate and impacts of MPs and associated chemicals in fish. It has been shown that exposure route can play an important role in particle-organism interactions and can determine the organismal uptake and localization of plastic particles in fish [Paper I]. Plastic nanoparticles interact with aquatic organisms: they can enter fish via contaminated prey (trophic transfer) and they can be directly ingested and/or adhere to organismal surfaces. Ingested nanoplastics can accumulate in the gastrointestinal tract and can then be internalized by the intestinal cells. Plastic ingestion is regarded as an environmentally relevant particle pathway in fish, and it facilitates their entrance into aquatic food chains. Studies included in this thesis also explored biological effects derived from the ingestion of larger, micro-sized plastic particles, at sizes commonly extracted from biological and environmental matrices, and which entail environmentally relevant chemical exposures [Papers II-III]. Direct impacts resulting from MP ingestion were found to be negligible, as no adverse effects were observed on fish intestinal physiology. Indirect, chemical exposure related effects resulting from ingestion of contaminated MPs were also minor. No indications of hepatic stress (oxidative stress, detoxification, endocrine disruption) were observed. It was concluded that MPs did not act as mechanical and chemical hazards upon ingestion, and are unlikely to cause adverse effects on organismal health. Although MPs showed capacity to associate with environmental contaminants [Papers II-IV], the transfer of pollutants from particles into fish via ingestion, as well as accumulation and biological impacts were suspected to be low [Papers II-IV]. The early findings presented in this thesis suggest that ingestion of MPs by commercial fish species does not significantly diminish the oxidative stability of commercial fish products, and MP-mediated chemical exposure does not pose an evident concern for human food quality and product shelf-life

    Determining ecotoxicity drivers and biodegradation kinetics of discharged chemicals in produced water from oil and gas extraction in the North Sea

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    Since the late 1990’s the “zero harmful discharge” regime related to offshore oil and gas extraction has been implemented on the Norwegian Continental Shelf. It has also gained traction in other areas of the North Sea due to OSPAR regulations. However, the holistic understanding of ecotoxicity drivers and biodegradation kinetics of this complex mixture is still lacking. The main goal of the MERIT project (Intelligent testing strategy for Minimizing EnviRonmental ImpacTs of produced water) was to develop a method for the quantitative estimation of drivers and the potential for reducing environmental impacts to acceptable levels. We summarize the findings of the project with focus on 1) identifying ecotoxicity drivers through whole effluent testing supported by toxicity identification evaluation and 2) determining environmentally relevant biodegradation kinetics of discharged chemicals in produced water. We present a testing strategy using empirical data and samples from five different platforms in the North Sea to align with the goals of minimizing environmental impacts of produced water
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