Peer review of the pesticide risk assessment of the active substance fish oil.

The conclusions of EFSA following the peer review of the initial risk assessments carried out by the competent authorities of the rapporteur Member State the Czech Republic and co-rapporteur Member State France for the pesticide active substance fish oil and the considerations as regards the inclusion of the substance in Annex IV of Regulation (EC) No 396/2005 are reported. The context of the peer review was that required by Commission Implementing Regulation (EU) No 844/2012, as amended by Commission Implementing Regulation (EU) No 2018/1659. The conclusions were reached on the basis of the evaluation of the representative uses of fish oil as a game repellent on deciduous and coniferous trees in forestry. The reliable end points, appropriate for use in regulatory risk assessment, are presented. Missing information identified as being required by the regulatory framework is listed.

Peer review of the pesticide risk assessment for the active substance acibenzolar-S-methyl in light of confirmatory data submitted.

The conclusions of the EFSA following the peer review of the initial risk assessment carried out by the competent authority of the rapporteur Member State, France, for the pesticide active substance acibenzolar-S-methyl are reported. The context of the peer review was that requested by the European Commission following the submission and evaluation of confirmatory information with regard to the endocrine disruption potential of the substance. The conclusions were reached on the basis of the evaluation of the representative uses of acibenzolar-S-methyl as a plant activator on pome fruit, tomato and tobacco. The reliable endpoints concluded as being appropriate for use in regulatory risk assessment, derived from the available studies and literature in the dossier peer reviewed, are presented. Assessments not finalised together with the missing information identified as being required by the regulatory framework are listed.

Comparative genotoxic evaluation of 2-furylethylenes and 5-nitrofurans by using the comet assay in TK6 cells.

The genotoxicity of three 2-furylethylene derivatives and four 5-nitrofurans was evaluated by using the comet assay in human lymphoblastoid cultured TK6 cells. The 2-furylethylene derivatives were 2-furyl-1-nitroethene, 1-(5-bromofur-2-yl)-2-nitroethene and 1-(5-bromofur-2-yl)-2-bromo-2-nitroethene, while the 5-nitrofurans were nitrofurantoin, nitrofurazone, furazolidone and 5-nitro-2-furanacrolein. The treatments lasted for 3 h in the absence of metabolic activation. No genotoxic effects were observed for two of the 2-furylethylene compounds, while the derivative 1-(5-bromofur-2-yl)-2-nitroethene showed a statistically significant response mainly at the highest concentration tested; this effect was considered biologically relevant and the compound was classified as slightly genotoxic. On the other hand, for the classical 5-nitrofurans tested there is a tendency towards a dose-related increase of the DNA damage in the comet assay and the observed increases for the parameters analysed (Olive tail moment, tail % DNA and tail length) were significant for all compounds. Then, the four 5-nitrofurans tested were considered genotoxic. These results show that the position of the nitro group influences the genotoxicity of the assayed compounds. Thus, in this comet assay, the 2-furylethylene derivatives having the nitro group attached outside the furan ring appear to be much less genotoxic than the 5-nitrofurans.

The mutagenic potential of the furylethylene derivative 2-furyl-1-nitroethene in the mouse bone marrow micronucleus test.

The compound 2-furyl-1-nitroethene (G-0) has been tested to determine its ability to induce clastogenic or aneugenic effects in vivo, through the induction of micronucleated polychromatic erythrocytes (MNPCE) in mouse bone marrow. Groups of five CD-1 male mice were administered once intraperitoneally at a dose range of 5-20 mg/kg and bone marrow was sampled at 24 and 48 h after the treatment. G-0 was dissolved in corn oil, thus a vehicle control group received only corn oil at 10 ml/kg. The positive control group was administered with cyclophosphamide (40 mg/kg). All animals dosed with the highest concentration of the test agent (20 mg/kg) showed evident clinical symptoms of toxicity. Although evidences of bone marrow toxicity were observed, no statistically significant increases in the incidence of MNPCE over the vehicle control group were observed at any sampling time with any of the assayed doses of the G-0 compound. Cyclophosphamide treatment increased the incidence of MNPCE in all treated animals, demonstrating the sensitivity of the assay conditions in which it was carried out. From the results obtained, it is concluded that the test agent G-0 is neither clastogenic nor aneugenic in the erythrocytes from the bone marrow of treated mice at the doses tested.