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Sökning: onr:"swepub:oai:DiVA.org:oru-48135" > The value of zebraf...

LIBRIS Formathandbok  (Information om MARC21)
FältnamnIndikatorerMetadata
00005926naa a2200421 4500
001oai:DiVA.org:oru-48135
003SwePub
008160209s2015 | |||||||||||000 ||eng|
024a https://urn.kb.se/resolve?urn=urn:nbn:se:oru:diva-481352 URI
024a https://doi.org/10.1186/s12302-015-0040-y2 DOI
040 a (SwePub)oru
041 a engb eng
042 9 SwePub
072 7a ref2 swepub-contenttype
072 7a for2 swepub-publicationtype
100a Di Paolo, Carolinau Department of Ecosystem Analysis, Institute for Environmental Research, ABBt - Aachen Biology and Biotechnology, RWTH Aachen University, Aachen, Germany4 aut
2451 0a The value of zebrafish as an integrative model in effect-directed analysis :b a review
264 c 2015-03-14
264 1b Springer,c 2015
338 a print2 rdacarrier
520 a Bioassays play a central role in effect-directed analysis (EDA), and their selection and application have to consider rather specific aspects of this approach. Meanwhile, bioassays with zebrafish, an established model organism in different research areas, are increasingly being utilized in EDA. Aiming to contribute for the optimal application of zebrafish bioassays in EDA, this review provides a critical overview of previous EDA investigations that applied zebrafish bioassays, discusses the potential contribution of such methods for EDA and proposes strategies to improve future studies. Over the last 10 years, zebrafish bioassays have guided EDA of natural products and environmental samples. The great majority of studies performed bioassays with embryos and early larvae, which allowed small-scale and low-volume experimental setups, minimized sample use and reduced workload. Biotesting strategies applied zebrafish bioassays as either the only method guiding EDA or instead integrated into multiple bioassay approaches. Furthermore, tiered biotesting applied zebrafish methods in both screening phase as well as for further investigations. For dosing, most of the studies performed solvent exchange of extracts and fractions to dimethyl sulfoxide (DMSO) as carrier. However, high DMSO concentrations were required for the testing of complex matrix extracts, indicating that future studies might benefit from the evaluation of alternative carrier solvents or passive dosing. Surprisingly, only a few studies reported the evaluation of process blanks, indicating a need to improve and standardize methods for blank preparation and biotesting. Regarding evaluated endpoints, while acute toxicity brought limited information, the assessment of specific endpoints was of strong value for bioactivity identification. Therefore, the bioassay specificity and sensitivity to identify the investigated bioactivity are important criteria in EDA. Additionally, it might be necessary to characterize the most adequate exposure windows and assessment setups for bioactivity identification. Finally, a great advantage of zebrafish bioassays in EDA of environmental samples is the availability of mechanism- and endpoint-specific methods for the identification of important classes of contaminants. The evaluation of mechanism-specific endpoints in EDA is considered to be a promising strategy to facilitate the integration of EDA into weight-of-evidence approaches, ultimately contributing for the identification of environmental contaminants causing bioassay and ecological effects.
650 7a NATURVETENSKAPx Geovetenskap och miljövetenskapx Miljövetenskap0 (SwePub)105022 hsv//swe
650 7a NATURAL SCIENCESx Earth and Related Environmental Sciencesx Environmental Sciences0 (SwePub)105022 hsv//eng
653 a Effect-directed analysis; Bioassay-guided fractionation; Zebrafish; Embryo; Larva; Bioassay; In vitro ; In vivo
653 a Enviromental Science
653 a Miljövetenskap
700a Seiler, Thomas B.u Department of Ecosystem Analysis, Institute for Environmental Research, ABBt - Aachen Biology and Biotechnology, RWTH Aachen University, Aachen, Germany4 aut
700a Keiter, Steffen,d 1971-u Örebro universitet,Institutionen för naturvetenskap och teknik,Department of Ecosystem Analysis, Institute for Environmental Research, ABBt - Aachen Biology and Biotechnology, RWTH Aachen University, Aachen, Germany,MTM4 aut0 (Swepub:oru)sfkr
700a Hu, Mengu Helmholtz-Zentrum für Umweltforschung (UFZ), Helmholtz Centre for Environmental Research, Leipzig, Germany4 aut
700a Muz, Melisu Helmholtz-Zentrum für Umweltforschung (UFZ), Helmholtz Centre for Environmental Research, Leipzig, Germany4 aut
700a Brack, Werneru Helmholtz-Zentrum für Umweltforschung (UFZ), Helmholtz Centre for Environmental Research, Leipzig, Germany4 aut
700a Hollert, Henneru Department of Ecosystem Analysis, Institute for Environmental Research, ABBt - Aachen Biology and Biotechnology, RWTH Aachen University, Aachen, Germany; College of Resources and Environmental Science, Chongqing University Beibei, Chongqing, China; College of Environmental Science and Engineering and State Key Laboratory of Pollution Control and Resource Reuse, Tongji University, Shanghai, China; State Key Laboratory of Pollution Control and Resource Reuse, School of the Environment, Nanjing University, Nanjing, China4 aut
710a Department of Ecosystem Analysis, Institute for Environmental Research, ABBt - Aachen Biology and Biotechnology, RWTH Aachen University, Aachen, Germanyb Institutionen för naturvetenskap och teknik4 org
773t Environmental Sciences Europed : Springerg 27:8, s. 1-11q 27:8<1-11x 2190-4707x 2190-4715
856u https://doi.org/10.1186/s12302-015-0040-yy Fulltext
856u https://enveurope.springeropen.com/track/pdf/10.1186/s12302-015-0040-y
8564 8u https://urn.kb.se/resolve?urn=urn:nbn:se:oru:diva-48135
8564 8u https://doi.org/10.1186/s12302-015-0040-y

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