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Dans le cadre du projet PROTEGE une enquête a été réalisée à Maré par l’Agence néo-Calédonienne de la Biodiversité (ANCB) auprès des chasseurs de chèvres ensauvagées. Les objectifs sont d’évaluer les pratiques et l’effort de chasse, le niveau de prélèvements, la capacité et la volonté de diversifier les techniques de chasse et à augmenter l’effort de chasse, au regard des dégâts constatés. Les chèvres ensauvagées (ou férales, Capra hircus) contribuent à la raréfaction de nombreuses espèces végétales natives et à la dispersion et au développement de plusieurs plantes introduites envahissantes. Aux Îles Loyauté des troupeaux de chèvres sont présents sur une grande partie des corniches littorales de Lifou et de Maré, où la chasse de la chèvre ensauvagée répond principalement à un besoin pour les dons et coutumes, et pour l’autoconsommation. Une pré-enquête a été réalisée par l’animateur PROTEGE (également agent de l’ANCB), afin de recenser les chasseurs de chèvres férales sur Maré et de prendre leurs contacts pour la réalisation de l’enquête. Dans un deuxième temps, l’ensemble des chasseurs de chèvres ensauvagées identifiés ont été contactés afin de répondre à l’enquête.

House sparrows (Passer domesticus) compete with native bird species, consume crops, and are vectors for diseases in areas where they have been introduced. Sparrow eradication attempts aimed at eliminating these negative effects highlight the importance of deploying multiple alternative methods to remove individuals while maintaining the remaining population naïve to techniques. House sparrow eradication was attempted from Robinson Crusoe Island, Chile, in the austral winter of 2012 using an experimental approach sequencing passive multi-catch traps, passive single-catch traps, and then active multi-catch methods, and finally active single-catch methods. In parallel, multiple detection methods were employed and local stakeholders were engaged. The majority of removals were via passive trapping, and individuals were successfully targeted with active methods (mist nets and shooting). Automated acoustic recording, point counts and camera traps declined in power to detect individual sparrows as the population size decreased; however, we continued to detect sparrows at all population densities using visual observations, underscoring the importance of local residents’ participation in monitoring. Four surviving sparrows were known to persist at the conclusion of eff orts in 2012. Given the lack of formal biosecurity measures within the Juan Fernández archipelago, reinvasion is possible. A local network of citizen observers is the best tool available to detect house sparrows at low density, however ongoing, dedicated eradication funding does not exist. Opportunistic removals via shooting have been possible from 2013–2016, but elusive individual sparrows were seen during a small number of days each year suggesting remnant group(s) exist in yet unknown forest locations.

This plan sets out the operational detail, logistics and framework for a planned eradication of introduced Pacific rats from Late Island (1,731ha) in the Kingdom of Tonga. The method for the eradication is the delivery of grain-based bait containing the anticoagulant brodifacoum, into every potential rodent territory on the island. This will be done during the driest part of the year when rodents are potentially most vulnerable due to lower relative availability of natural food supplies. Because of the island’s size and complex topography, the bait will be applied aerially using a helicopter with an underslung bait spreading bucket. Aerial application has been successful in eradicating rodents from many islands around the world, and the logistics and methodology are based upon similar successful operations. Mitigation measures will be required for key non-target species, especially the Friendly-ground dove. Monitoring of rodents and native species before and after the operation will be required to assess the success and effect of the operation.