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Do cytotoxicity and cell death cause false positive results in the in vitro comet assay?

Azqueta, Amaya ; Stopper, Helga; Zegura, Bojana; Dusinska, Maria; Møller, Peter

The comet assay is used to measure DNA damage induced by chemical and physical agents. High concentrations of test agents may cause cytotoxicity or cell death, which may give rise to false positive results in the comet assay. Systematic studies on genotoxins and cytotoxins (i.e. non-genotoxic poisons) have attempted to establish a threshold of cytotoxicity or cell death by which DNA damage results measured by the comet assay could be regarded as a false positive result. Thresholds of cytotoxicity/cell death range from 20% to 50% in various publications. Curiously, a survey of the latest literature on comet assay results from cell culture studies suggests that one-third of publications did not assess cytotoxicity or cell death. We recommend that it should be mandatory to include results from at least one type of assay on cytotoxicity, cell death or cell proliferation in publications on comet assay results. A combination of cytotoxicity (or cell death) and proliferation (or colony forming efficiency assay) is preferable in actively proliferating cells because it covers more mechanisms of action. Applying a general threshold of cytotoxicity/cell death to all types of agents may not be applicable; however, 25% compared to the concurrent negative control seems to be a good starting value to avoid false positive comet assay results. Further research is needed to establish a threshold value to distinguish between true and potentially false positive genotoxic effects detected by the comet assay.

2022

Do perfluorinated compounds in dust from Norwegian houses affect the serum levels of their residents? NILU F

Haug, L.S.; Huber, S.; Schlabach, M.; Becher, G.; Thomsen, C.

2010

Do photochemical clocks keep time? The interaction of mixing and aging in the troposphere. NILU PP

Parrish, D.D.; Stohl, A.; Forster, C.; Atlas, E.L.; Goldan, P.D.; Kuster, W.C.

2005

Do physiography and hydrology determine the physico-chemical properties and trophic status of coastal lagoons? A comparative approach.

Roselli, L.; Cañedo-Argüelles, M.; Costa Goela, P.; Cristina, S.; Rieradevall, M.; D'Adamo, R.; Newton, A.,.

2013

Does climate change and seasons have an influence the accumulation of contaminants in Arctic marine pelagic food webs?

Hallanger, I.G.; Ruus, A.; Warner, N.A.; Evenset, A.; Gabrielsen, G.W.; Borgå, K.

2011

Does contaminant exposure disrupt maternal hormones deposition? A study on per- and polyfluoroalkyl substances in an Arctic seabird

Jouanneau, William; Léandri-Breton, Don-Jean; Herzke, Dorte; Moe, Børge; Nikiforov, Vladimir; Pallud, Marie; Parenteau, Charline; Gabrielsen, Geir Wing; Chastel, Olivier

Elsevier

2023

Does the EU migration level of chromium VI in toys need to be lowered? Commentary.

Scientific Committee on Health, Environmental Risks (SCHER): Bartonova, A.; Beausoleil, C.; Carroquino, M.J.; De Voogt, P.; Duarte-Davidsona, R.; Fernandes, T.; Gzyl, J.; Janssen, C.; Krätke, R.; Linders, J.; Schoeters, G.

2015

Domestic heating: an important source of air pollution in European urban areas.

Guerreiro, C.; de Leeuw, F.; Horalek, J.; Viana, M.

2015

Domestic heating: an important source of particulate matter pollution.

Guerreiro, C.; de Leeuw, F.; Horálek, J.; Viana, M.

2015

Dose calculations for aviation using atmospheric transport modelling and radioprotection tools

Vargas, Arturo; Arnold, Delia; Evangeliou, Nikolaos; Maurer, Christian; Duch, Maria Amor

2018

Dose calculations in aircrafts after Fukushima nuclear power plant accident – Preliminary study for aviation operations

Vargas, Arturo; Arnold, Delia; Duch, M.-A.; Evangeliou, Nikolaos; Sievers, Klaus; Maurer, C

There is little information to decision support in air traffic management in case of nuclear releases into the atmosphere. In this paper, the dose estimation due to both, external exposure (i.e. cloud immersion, deposition inside and outside the aircraft), and due to internal exposure (i.e, inhalation of radionuclides inside the aircraft) to passengers and crew is calculated for a worst-case emergency scenario. The doses are calculated for different radionuclides and activities. Calculations are mainly considered according to International Commission on Radiological Protection (ICRP) recommendations and Monte Carlo simulations. In addition, a discussion on potential detectors installed inside the aircraft for monitoring the aerosol concentration and the ambient dose equivalent rate, H*(10), for during-flight monitoring and early warning is provided together with the evaluation of a response of a generic detector. The results show that the probability that a catastrophic nuclear accident would produce significant radiological doses to the passengers and crew of an aircraft is very low. In the worst-case scenarios studied, the maximum estimated effective dose was about 1 mSv during take-off or landing operations, which is the recommended yearly threshold for the public. However, in order to follow the ALARA (As Low As Reasonably Achievable) criteria and to avoid aircraft contamination, the installation of radiological detectors is considered. This would, on one hand help the pilot or corresponding decision maker to decide about the potential change of the route and, on the other, allow for gathering of 4D data for future studies.

Elsevier

2019

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