Dispersal, landscape and travelling waves in cyclic vole populations.

Travelling waves (TW) are among the most striking ecological phenomena emerging in oscillating populations. Despite much theory, understanding how real-world TW arise remains a challenge for ecology. Herein, we analyse 16-year time series of cyclic vole populations collected at 314 localities covering 2500 km² in France. We found evidence for a linear front TW spreading at a speed of 7.4 km year(-1) along a north-west/south-east direction and radiating away from a major landscape discontinuity as predicted by recent theory. The spatial signature of vole dispersal was assessed using genetic data collected at 14 localities. Both data sets were handled using similar autocorrelation approaches. Our results revealed a remarkable congruence of the spatial extent and direction of anisotropy of both demographic and genetic structures. Our results constitute the first empirical evidence that effective dispersal is limited in the direction of TW while most of the individual exchanges occur along the wave front.

Kinetics of bromadiolone in rodent populations and implications for predators after field control of the water vole, Arvicola terrestris.

We document the kinetics of bromadiolone in two rodent populations after a field control of water voles, and their implications for predator exposure. Water voles and common voles were trapped aboveground and underground from 1 to 135 days after bromadiolone treatment in the field. Livers, digestive tracts, and rests of the body were analyzed separately. Our results indicate that 99.6% of the water voles trapped underground and 41% of the common voles trapped aboveground contain bromadiolone residues. Concentrations were maximal between 3.3 and 6.5 days after treatment, according to the tissues examined and the model applied for water voles, and after 1.3 to 3.7 days for common voles. Water voles appeared available almost exclusively for foraging predators. Common voles, found less likely to be poisoned and exhibiting weaker concentrations, were mainly sampled aboveground. The liver, primarily eaten by some predators and scavengers, contains a larger bromadiolone quantity (59% of the total amount found in water voles). The rejection of the digestive tract by those species may lead to a subsequent consumption of voles with higher bromadiolone concentrations (from +3.8 to +5.8% of concentration) and provide a moderate risk increase. After 135 days, eight of the ten water voles and one of the two common voles exhibited detectable residues. Additionally, one specimen presented higher concentrations than the others, and similar to those measured in Voles trapped between the first 15-20 days. This may have consequences on predator intoxications several months after treatment. These results integrate individual differences for the two main rodent species present in treated areas. Implications for predator exposure were investigated at the end of the study and suggest that, if the risk of secondary poisoning is maximal during the first 15-20 days when the rodent densities remain high, exposure conditions are maintained for at least 135 days.

How environment and vole behaviour may impact rodenticide bromadiolone persistence in wheat baits after field controls of Arvicola terrestris?

We aimed to evaluate whether environmental factors affect the persistence of bromadiolone in baits in field treatment. Baits were distributed in three soils according to two types of distribution: (1) artificial galleries conform to agricultural practices; (2) storage cavities to mimic bait storage by voles. Persistence was evaluated for 30 days in galleries and 80 days in storage cavities in autumn and spring. The decrease of bromadiolone concentrations was described by a first-order kinetic model. In galleries, the half-lives ranged from 3.0 to 5.1 days in autumn and from 5.4 to 6.2 days in spring. The half-lives were similar between soils and seasons but the pattern of persistence differed lightly for two soils between seasons. Half-lives in storage cavities, 42.7 and 24.6 days in autumn and spring respectively, were longer than in galleries. To conclude, both soil characteristics and climatic conditions weakly influence persistence, while bait storage lengthens it dramatically.

Persistence of bromadiolone anticoagulant rodenticide in Arvicola terrestris populations after field control.

This paper documents the exposure pattern of a population of small mammals to bromadiolone over time in a field-scale follow up. This is the first assessment of the field-scale effect of such control operation on the availability of bromadiolone-exposed A. terrestris prey to nontarget predator species. It indicates that an important risk of poisoning of nontarget species does exist during large-scale field control operations with bromadiolone, which is contradictory to results obtained from laboratory experiments in the early 1980s and consistent with the secondary poisoning hazards due to repeated exposure regularly reported during the past 20 years.