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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.)

,

FAO

,

Glencross, Kevin (Dr.)

,

Hancock, Wayne (Dr.)

,

Kete, Tevita

,

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.
Improving the breeding success of a colonial seabird: a cost-benefit comparison of the eradication and control of its rat predator
BRB
Available Online

Bretagnolle, Vincent.

,

Culioli, Jean-Michel.

,

Lorvelec, Olivier.

,

Pascal, Michel Pascal.

2008
Breeding success of 5 Cory’s shearwater Calonectris diomedea sub-colonies of Lavezzu Island (Lavezzi Archipelago, Corsica) was checked annually for 25 consecutive years from 1979 to 2004. Between 1989 and 1994, 4 ship rat Rattus rattus controls were performed in several subcolonies. In November 2000, rats were eradicated from Lavezzu Island and its 16 peripheral islets (85 ha) using traps then toxic baits. We compare cost (number of person-hours required in the field) and benefit (Cory’s shearwater breeding success) of control and eradication. The average breeding success doubled when rats were controlled or eradicated (0.82) compared to the situation without rat management (0.45). Moreover, the average breeding success after eradication (0.86) was significantly (11%) higher than after rat controls (0.75). Furthermore, the great variation in breeding success recorded among sub-colonies both with and without rat control declined dramatically after eradication, suggesting that rats had a major impact on breeding success. The estimated effort needed to perform eradication and checking of the permanent bait-station system during the year following eradication was 1360 person-hours. In contrast, rat control was estimated to require 240 or 1440 person-hours per year when implemented by trained and untrained staff, respectively. Within 6 yr, eradication cost is lower than control cost performed by untrained staff and confers several ecological advantages on more ecosystem components than Cory’s shearwater alone. Improved eradication tools such as hand or aerial broadcasting of toxic baits instead of the fairly labour-intensive eradication strategy we used would dramatically increase the economic advantage of eradication vs. control. Therefore, when feasible, we recommend eradication rather than control of non-native rat populations. Nevertheless, control remains a useful management tool when eradication is not practicable.