Corruption is known to limit economic development and fuel poverty, but it may also hinder conservation efforts and contribute to biodiversity loss. Here we explore some of the ways that corruption may affect conservation. We argue that corruption has potentially significant implications that should be highlighted and tackled directly. Unfortunately, research into the topic lags behind that in other sectors and empirical studies are scarce and underdeveloped. The result is that, whilst some academics and practitioners cite corruption as a threat to biodiversity and call for efforts to increase transparency and accountability, we currently know little regarding the nature and magnitude of any effects it may have. Whilst precautionary measures can be built into conservation projects to pre-empt corruption, further research would help to shed light on this issue and aid the development of appropriate responses.

Smith & Walpole (2005) focus on a heretofore little examined issue of unknown importance: the role of corruption in affecting biodiversity conservation outcomes. Unfortunately, there are no well-executed empirical studies of the relationship between corruption and conservation to guide practitioners. As noted by Smith & Walpole, however, the role of corruption in affecting other economic outcomes has been the subject of numerous theoretical and empirical analyses. These other analyses offer useful insights to conservationists precisely because the biodiversity context is representative of a larger class of contexts in which power is delegated to self-interested bureaucrats. Readers interested in the topic would do well to take a close look at the references in Smith & Walpole, as well as visiting the World Bank's website on corruption and governance (World Bank, 2005).

Conservation is a complex process that is affected by culture, politics, economics and biology. Smith & Walpole (2005) are right to identify corruption as an important influence on conservation, and their goal, to stimulate debate and analysis of this problem, is meritorious. Here, I expand on three points to highlight some further complexities that arise from their work.

Corruption is a complex phenomenon with various confounding effects and, in their separate replies, both Ferraro (2005) and Katzner (2005) note that in some cases corruption may have short- and long-term benefits for conservation by limiting extractive and destructive development activities. We agree, and we also acknowledge that better governance does not necessarily lead to better conservation; a cursory look at Conservation International's biodiversity hotspots (Conservation Interational, 2005) shows that these threatened regions occur in countries with both high and low governance levels.

Data on habitat requirements of the threatened Eurasian bittern Botaurus stellaris are largely qualitative and limited to countries holding small populations. We assessed the habitat spectrum exploited by male bitterns during the breeding season, based on the analysis of 40 booming sites and 33 non-booming sites in 2,500 ha of heterogeneous reed-beds in the Camargue, France. Environmental variables contributing to booming site selection were, in decreasing order of importance, determined by their contribution to multivariate statistical models: water level in April, proportion of open water, density of dry and green reeds, percentage cover of non-reed species, salinity and turbidity of surface water, and reed height and diameter. Overall, booming sites were characterized by a homogeneous cover of relatively sparse green and dry reeds growing with other plant species in shallow (10–15 cm), clear water. Because these findings are contrary to the traditional perception of bittern habitat in Europe, a reassessment of the species' ecological requirements throughout its distributional range is warranted. In the Camargue the main factors involved in habitat selection (water level and dry reed density) are directly associated with site management, and bitterns respond rapidly to slight environmental changes.

Attitudes towards wild animals are reflected through history in various categorizations of species. For example, changes in the useful-harmful dichotomy of species have affected policy decisions during the long history of organized pest persecution as well as during the much more recent rise of nature conservation. The first hunting legislation in Finland dates back more than 650 years, to times when the country belonged to the Kingdom of Sweden. From those times to the early 20th century various acts of law exhibited a marked variation in placing species into useful and harmful categories. The dichotomy seems to be based upon fundamental ecological interactions between humans and other species. We show that the varying interest in pest persecution as well as important conservation milestones have been associated with contemporary human-animal relations such as the attitudes of decision makers and laymen towards wild animals, and the public awareness of species conservation issues.

In Finland, hunting bounties for pest animals were first introduced in the 1647 hunting law. Avian pests were included in bounty schemes a century later when a price was put on more than 20 species. The list of bounty species varied widely during the next 200 years. We examined the development of bounty schemes in Finnish wildlife management during 1647–1975 with respect to the prevailing attitudes to nature and hunting practices. We surveyed Finnish hunting legislation from the 1300s to the present, and collected hunting bounty data from hunting associations' archives and from statistics published in hunting magazines during the 19th and 20th centuries. Local municipalities and the government, and also hunters' and fishermen's organizations, paid bounties for pest species. Bounties were considered justified for direct and indirect economic, religious and ethical reasons. Organized persecution of pests was considered a necessary component of game management. The ‘golden age’ of bounty schemes from 1898 to the 1920s contributed to local extinctions of both mammalian and avian species. The cessation of law-based bounty schemes in 1975 was preceded by a period of strong environmental thinking, and bounty schemes were widely considered costly, outdated and unethical.

Hunting for subsistence and trade constitute a major threat to wildlife populations within and outside protected areas in Myanmar. We examined hunting patterns in a forested landscape adjoining the Hkakaborazi National Park in north Myanmar with the aim of generating recommendations to manage hunting. The results described here focus on two issues: the significance of proximity to settlements and markets for prey abundance, and the influence of relative abundance and intrinsic preference on prey offtake. We used strip transect and camera trap surveys to generate relative abundance indices and overall encounter/capture rates for commonly hunted species at four sites that differed in their proximity to settlements and large trading towns. Questionnaires were used to obtain meal records and information on hunting. Encounter and capture rates for hunted species appear to be inversely related to proximity to villages as well as to large, commercial towns. Hunting is indiscriminate, with offtake determined largely by relative abundance rather than intrinsic preference or legislation. Specific management and policy recommendations include the need to monitor the impacts of hunting on vulnerable species, the demarcation of no-take areas, and modification of the legal framework for wildlife conservation.

Irrawaddy dolphins Orcaella brevirostiris are found in coastal waters from the Bay of Bengal east to Palawan, Philippines and south to northern Australia. They also occur in three large tropical river systems in South-east Asia: the Mekong, Mahakam and Ayeyarwady. In March and May 1997 approximately 350 km of riverine habitat in parts of north-east Cambodia were surveyed, discussions took place with local people, and reported dry season dolphin habitat was mapped. Our objectives were to investigate the status, habitat and distribution of dolphins in north-east Cambodia and identify threats to the continued survival of dolphins in the Mekong River Basin. Nine groups of dolphins were observed in the Mekong River. A ‘best’ estimate of 40 animals were seen. Irrawaddy dolphins were generally confined to sections of the river with water levels >8–10 m during the dry season. It appears that the Mekong River dolphin population is rapidly declining. In 1997 there were probably no more than 100¨C150 dolphins left in north-east Cambodia (including southern Laos) and no more than 200 within the entire Mekong River Basin, although these numbers remain tentative. Anthropogenic mortality is high, albeit largely unintentional, and there is considerable risk that the dolphin population will become locally extinct in the Mekong River in the near future. The establishment of community-managed deep water Fish Conservation Zones with government support may represent the best opportunity for reducing dry season dolphin mortality from large-meshed gillnet entanglement. Efforts to establish protected areas for dolphins are currently underway.

Few viable populations of western black crested gibbon Nomascus concolor remain in southern China and northern Indochina, where the species is endemic. We conducted village surveys in the Nam Ha National Protected Area in Luang Namtha Province, Lao PDR to assess presence and status of gibbon populations. Forest surveys used to verify gibbon presence and species identification confirmed village reports of gibbon populations in three locations, and sonogram analysis identified all as N. concolor. These represent an expansion in the known distribution of western black crested gibbon in Lao PDR and the only known populations to occur inside the national protected area system. Significantly longer times since gibbons were last reported were associated with villages with <50% forest cover and high human populations. Although village taboos regarding gibbon hunting were reported, hunting and trade were nevertheless identified as factors contributing to gibbon decline. Results indicated that increased community-based management, public education and enforcement are needed to maintain N. concolor populations and their habitat in Lao PDR.

We describe improvements to monitoring/indexing methodology for predators of marine turtle nests on the east coast of Florida, and the resulting marine turtle conservation implications from integrating the methodology into predator management. A strip transect from dune line to the shore improved an already successful design for monitoring raccoons, and was also sensitive for armadillos. The data were integrated into predator management operations to effectively and efficiently remove the species responsible for turtle nest predation. Tracking plot data also served to validate predator patterns of behavior relative to turtle nesting and improve prospects for preventive predator management strategies. Perhaps the most important finding is that predation at a beach historically suffering nearly complete losses (95%) of marine turtle nests had nest predation reduced to nominal levels (9.4%). For 2002 this predation level represents an estimated 69,000 additional hatchling turtles produced over historical predation rates, and 16,700 additional hatchlings over the previous lowest predation rate.

Nature conservation can often be costly and the resources available are often less than are required. Resource allocations and expenditures for nature conservation have an opportunity cost in terms of foregone projects, but are rarely subjected to as much scrutiny as other public activities. Failure to apply economic tools to nature conservation decision making can result in errors in project selection, wasted use of scarce resources, and lower levels of conservation than it is possible to achieve from the resources available. In some instances where economics has been proposed for use in nature conservation research, the methodologies applied provide information that is of limited usefulness to decision makers. Non-market valuation has limited potential to help in nature conservation decision making, is costly to complete and should be supplanted by more useful techniques that focus on the cost and the payoff from nature conservation actions. In contrast, Cost Effectiveness Analysis and Cost Utility Analysis are practical tools that can provide valuable information for conservation decision makers and improve conservation achievement.

There are four known species of Isoetes (Family Isoetaceae) from China: I. hypsophila, I. sinensis and I. yunguiensis on the mainland, and I. taiwanensis on Taiwan. In a 4-year study we documented the distribution and habitat characteristics of all four species and evaluated their conservation status using IUCN criteria. All four species are facing a high risk of extinction and should be categorized as Critically Endangered on the IUCN Red List. Habitat degradation and loss, water pollution and eutrophication, competitive exclusion, and human disturbance are the main factors causing the decline and extirpation of Isoetes. Only I. taiwanensis is protected in situ in Yangmingshan National Park on Taiwan. None of the species or habitats of Isoetes on mainland China are presently protected, although all species have been designated by the government as State Key Protected Wild Plants. Our results suggest that conservation strategies should be implemented urgently, particularly on the mainland.

We report on seven new localities for Mantella bernhardi, a Malagasy poison frog that was previously known only from a single site. This species has been considered threatened with extinction because of ongoing habitat destruction and collection for the pet trade (up to c. 3,000 specimens per year). The new localities considerably extend the known range of this species, which has now been documented from c. 21.00° to 24.15°S and 47.00° to 48.00°E, and over 60–629 m altitude. Two of the sites are within protected areas (Ranomafana National Park and Manombo Special Reserve). An overlap analysis of the potential distribution area of the species, based on the extent of remaining primary vegetation, indicates that the habitat of M. bernhardi in south-eastern Madagascar is fragmented and populations may be relatively small and isolated. We support the IUCN Red List category of Endangered for this species and highlight the need for detailed studies of its populations.

Populations of harlequin frogs Atelopus are declining throughout their geographical range. In Peru six of the 11 nominally described species are Critically Endangered, and there are at least 17 undescribed additional forms (all representing apparently distinct species), the conservation status of which is unknown. Most Atelopus taxa in Peru have relatively small geographical ranges, some known only from single populations, and have only a limited chance of survival. Conservation will require: (1) improvement of the faunistic and taxonomic knowledge of the genus, (2) field surveys, including in remote areas, (3) assessment of all species and populations for chytridiomycosis and research on the agent's biology, (4) ex situ conservation measures to facilitate later reintroduction, and (5) involvement of national and international conservationists and local people.

Using the species-area correlation I predicted the percentage of endemic Amazonian mammals committed to extinction by 2020 as an outcome of deforestation resulting from the implementation of mega-infrastructure projects in the Brazilian Amazon. Simulations based on optimistic and non-optimistic deforestation scenarios showed a 2-fold and a 3-fold increase, respectively, in Amazonian mammals committed to extinction. The predicted number of threatened species by 2020 was 5–18% of the total number of endemic mammal species, depending on the scenario and equation used. This increase in extinction rates could be catastrophic for ecosystem stability in the Amazon because the loss of functional groups may produce a cascade effect of species extinctions.