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Abstract Background The aim of environmental risk assessment (ERA) for pesticides is to protect ecosystems by ensuring that specific protection goals (SPGs) are met. The ERA follows a prospective tiered approach, starting with the most conservative and simple step in risk assessment (RA) (so-called tier 1) using the lowest available appropriate endpoint derived from ecotoxicological tests. In 2015, for the tier 1 RA of aquatic primary producers, the recommendation was changed from using the lowest of the 50% inhibition (EC50) values based on biomass (area under the curve—EbC50), increase in biomass (yield- EyC50) or growth rate (ErC50) to only using the growth rate inhibition endpoint (ErC50) because it is independent of the test design and thus more robust. This study examines the implications of this such on the level of conservatism provided by the tier 1 RA and evaluates whether it ensures a suitable minimum protection level. Results Our analysis shows that replacing the lowest endpoint with the growth rate inhibition endpoint while maintaining the assessment factor (AF) of 10 significantly reduces the conservatism in the tier 1 RA. Comparing protection levels achieved with different endpoints reveals that the current assessment is less protective. To maintain the previous level of protection, and since the protection goals have not changed, we recommend to multiply the default AF of 10 by an extra factor of minimum 2.4 in the tier 1 RA based on ErC50. Independently of the endpoint selected in tier 1 RA, several issues in the general RA of pesticides contribute to uncertainties when assessing the protection levels, e.g., lack of appropriate comparison of the higher tier experimental studies (i.e., best achievable approximation of field situation, so-called surrogate reference tier) with field conditions or the regulatory framework's failure to consider realistic conditions in agricultural landscapes with multiple stressors and pesticide mixtures. Conclusions We advise to consider adjusting the risk assessment in order to reach at least the previous protection level for aquatic primary producers. Indeed continuing using an endpoint with a higher value and without adjustment of the assessment factor is likely to jeopardize the need of halting biodiversity loss in surface waters.

This paper proposes the computation of the Tate pairing, Ate pairing and its variations on the special Jacobi quartic elliptic curve Y2=dX4+Z4$Y^{2}=dX^{4}+Z^{4}$. We improve the doubling and addition steps in Miller's algorithm to compute the Tate pairing. We use the birational equivalence between Jacobi quartic curves and Weierstrass curves, together with a specific point representation to obtain the best result to date among curves with quartic twists. For the doubling and addition steps in Miller's algorithm for the computation of the Tate pairing, we obtain a theoretical gain up to 27%$27\%$ and 39%$39\%$, depending on the embedding degree and the extension field arithmetic, with respect to Weierstrass curves and previous results on Jacobi quartic curves. Furthermore and for the first time, we compute and implement Ate, twisted Ate and optimal pairings on the Jacobi quartic curves. Our results are up to 27%$27\%$ more efficient compared to the case of Weierstrass curves with quartic twists.

In this work, we are interested in arithmetic on large prime field and their extensions of small degree. We explain why it is very interesting to use RNS arithmetic for the base field 𝔽p when computations in 𝔽pk have to be done, essentially thanks to lazy reduction. This is for example the case for pairing computations on ordinary curves (as MNT or BN curves). We show that using RNS can considerably decrease the number of basic operations required for a pairing computation in many popular situations.

Le recyclage des matières plastiques constitue un enjeu environnemental majeur en raison de la diminution des ressources pétrolières et du problème de la gestion des déchets en fin de vie. Toutefois, ce recyclage est rendu difficile par la présence d'additifs ou de pollutions au sein des polymères. L'objectif de cette communication est de présenter et de commenter deux principaux exemples permettant d'illustrer l'influence de la présence de contaminants sur les propriétés du matériau recyclé. Dans un cas, on étudiera l'influence de la méthode de recyclage sur les propriétés finales du matériau et dans l'autre cas, on cherchera à remédier à la diminution des propriétés mécaniques du polymère recyclé en compatibilisant le contaminant au sein du matériau plastique. The recycling of plastic materials represents a major environmental challenge due to the decrease of petroleum resources and the problem of end-of-life products management. However, the presence of additives or pollutants inside polymers generally makes the recycling more difficult. The aim of the presentation is to describe two main examples illustrating the influence of the presence of contaminants on the properties of recycled polymers. First, the influence of the recycling method on the final properties of the material will be studied. Then, the decrease of the mechanical properties of the recycled polymer will be overcome by compatibilizing the contaminant inside the plastic material.