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The history of the aerial application of rodenticide in New Zealand
Biodiversity Conservation, BRB
Available Online

Broome, K.

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Garden, P.

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McClelland, P.

2019
Following the incursion of rats (Rattus rattus) on Taukihepa (Big South Cape Island; 93.9 km²) off southern New Zealand in 1963, and the subsequent extirpation of several endemic species, the New Zealand Wildlife Service realised that, contrary to general belief at the time, introduced predators do not reach a natural balance with native species and that a safe breeding habitat for an increasing number of ‘at risk’ species was urgently needed. Off shore islands offered the best option for providing predator free habitat but there was a limited number of predator-free islands available and most were very small. Eradicating rodents on larger islands to provide a wider range and greater area of habitats was required and hand treating these larger areas using trapping and hand application of toxicants, the only methods available at the time, proved problematic and often impossible. Helicopters had been used to distribute bait for the control of rabbits and brushtail possums in the past but eradication of any particular predator species was considered ‘not feasible’. The development of a GPS-based aircraft guidance system, a suitable bait product, specialised bait delivery systems and second-generation anti-coagulant toxicants changed that. Now islands as large as South Georgia (3,900 km²) have been treated using this method
House mice on islands: management and lessons from New Zealand
Biodiversity Conservation, BRB
Available Online

Birmingham,C.

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Broome, K.

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Brown, D.

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Brown, K.

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Corson, P.

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Cox, A.

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Golding, C.

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Griffiths, R.

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Murphy, E.

2019
The impacts of house mice (Mus musculus), one of four invasive rodent species in New Zealand, are only clearly revealed on islands and fenced sanctuaries without rats and other invasive predators which suppress mouse populations, influence their behaviour, and confound their impacts. When the sole invasive mammal on islands, mice can reach high densities and influence ecosystems in similar ways to rats. Eradicating mice from islands is not as difficult as previously thought, if best practice techniques developed and refined in New Zealand are applied in association with diligent planning and implementation. Adopting this best practice approach has resulted in successful eradication of mice from several islands in New Zealand and elsewhere including some of the largest ever targeted for mice; in multi-species eradications; and where mouse populations were still expanding after recent invasion. Prevention of mice reaching rodent-free islands remains an ongoing challenge as they are inveterate stowaways, potentially better swimmers than currently thought, and prolific breeders in predator-free habitat. However, emergent mouse populations can be detected with conventional surveillance tools and eradicated before becoming fully established if decisive action is taken early enough. The invasion and eventual eradication of mice on Maud Island provides a case study to illustrate New Zealand-based lessons around mouse biosecurity and eradication.
Feasibility of eradicating the large white butterfly (Pieris brassicae) from New Zealand: data gathering to inform decisions about the feasibility of eradication
Biodiversity Conservation, BRB
Available Online

Broome, K.

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Brown, K.

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Green, C.

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Phillips, C.B.

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Toft, R.

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Walker, G.

2019
Pieris brassicae, large white butter?y, was ?rst found in New Zealand in Nelson in May 2010. The Ministry for Primary Industries (MPI) responded with a monitoring programme until November 2012 when the Department of Conservation (DOC) commenced an eradication programme. DOC was highly motivated to eradicate P. brassicae by the risk it posed to New Zealand endemic cress species, some of which are already nearly extinct. DOC eliminated the butter?y from Nelson in less than four years at a cost of ca. NZ$5 million. This is the ?rst time globally that a butter?y has been purposefully eradicated. Variation in estimates of bene?ts, costs, the e?cacy of detection and control tools, and the probability of eradication success all contributed to uncertainty about the feasibility. Cost bene?t analyses can contribute to assessing feasibility but are prone to inaccurate assumptions when data are limited, and other feasibility questions are equally important in considering the best course of action. Uncertainty does not equate to risk and reducing uncertainty through data gathering can inform feasibility and decision making while increasing the probability of eradication success.
Sustainable livelihood strategies for conservation of biodiversity in Fiji, including potential crops and value adding opportunities in three FPAM project sites - Marketing of suitable products and recommendations; across three project sites: Greater Tomaniivi Protected Areas on Viti Levu, Greater Delaikoro Protected Areas on Vanua Levu, Taveuni Forest Reserve/Ravilevu Nature Reserve on Taveuni.
Biodiversity Conservation
Available Online

Addinsall, Cherise (Dr.)

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FAO

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Glencross, Kevin (Dr.)

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Hancock, Wayne (Dr.)

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Kete, Tevita

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Prasad, Vinesh

2017
Conservation of biodiversity, improving rural livelihoods and supporting sustainable agriculture are key issues globally, but for many Pacific Island Countries (PICs) key biodiversity reserves are under considerable pressure from clearing and degradation. Rural communities are often put in a situation where clearing of forest margins is undertaken to meet demand for arable land to produce food and generate income. Forest reserves are also degraded by logging, where timber royalties are important in the absence of other sources of income for traditional landowners and communities. Therefore, agroforestry and ecologically based agriculture systems in the forest margins can help to offset reliance on forest degradation and can enhance the buffers around key reserves. Sustainable forest management and ecotourism also need to be maximised to help meet these challenges of generating income whilst maintaining or enhancing biodiversity, conserving soil and water resources.
Mainstreaming Ecosystem Services and Biodiversity into Agricultural Production and Management in the Pacific Islands - Technical guidance document
Biodiversity Conservation
Available Online

FAO

2016
The international community is increasingly aware of the link between biodiversity and sustainable development and its direct impact on wealth, health and well-being. Biodiversity is the origin of all crops and domesticated livestock. It is also the source of vital ecosystem services and functions, including soil conservation, water cycling, pollination, pest and disease regulation, carbon sequestration and nitrogen fixation. Biodiversity and the ecosystem services it supports are thus key to nutritional diversity and to agricultural productivity and resilience. The Convention on Biological Diversity (CBD) Strategic Plan for Biodiversity 2011–2020 and its 20 Aichi Biodiversity Targets provide a framework for countries to develop national targets and policies for sustaining biodiversity for a healthy planet. To meet rising global food demands, agricultural systems need to produce greater quantities of more diverse and nutritious food in a sustainable way. This progress can and must be achieved without driving biodiversity loss. It must come through gains in the efficiency of resource use, through sustainable intensification and a landscape perspective in agricultural production. By contributing to the conservation and sustainable use of biodiversity, agriculture will be a key driver for eliminating poverty, improving human health and providing energy, food and clean water for all while maintaining natural ecosystems.