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Abstracts available here - Society for Conservation Biology

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25th International Congress <strong>for</strong> <strong>Conservation</strong> <strong>Biology</strong> • Auckland, New Zealand • 5-9 December 2011<br />

communities to tackle biodiversity issues.<br />

2011-12-08 18:30 Rare plant populations on degraded and natural<br />

habitat do not respond equally to mitigation of pest and pathogen<br />

pressure<br />

Squires, S, of Environment and <strong>Conservation</strong>, Government<br />

of Newfoundland and Labrador, Corner Brook, NL, Canada;<br />

Hermanutz, L*, Department of <strong>Biology</strong>, Memorial University, St.<br />

John’s, NL, Canada A1B 3X9; Dixon, P, 3Agriculture and Agri-Food<br />

Canada, St. John’s, NL, Canada;<br />

Populations of the Limestone Barrens endemics, Braya longii (endangered)<br />

and B. fernaldii (threatened) have declined since 1998. Stage based<br />

transition matrices created from nine years of demographic data and<br />

summarized into deterministic projections suggest additional declines over<br />

the next 10 years <strong>for</strong> each Braya species. The viability of populations on<br />

natural substrate is vulnerable to increased mortality of large, flowering<br />

plants, w<strong>here</strong> as populations on anthropogenically degraded substrate are<br />

vulnerable to declines in seedling survival and seed production. Between<br />

2003 and 2006 the impacts of a non-native insect and pathogenic threats<br />

on Braya reproduction and survival was determined. Management<br />

scenarios were explored by adjusting the baseline viability models to reflect<br />

the survival rates of unaffected plants. For populations on natural substrate,<br />

the removal of the insect improved population growth rate more than the<br />

removal of a pathogen (B. longii- 8.0% vs 1.8%, B. fernaldii- 10.0% vs<br />

0.3%), w<strong>here</strong> as on anthropogenically degraded substrate the removal of<br />

a pathogen improved the population growth rate more than the removal<br />

of the insect (B. longii- 1.8% vs 1.1%, B. fernaldii- 10.7% vs 7.4%).<br />

Intervention, including the prevention of mortality due to pests and the<br />

restoration of populations will help improve long-term population viability.<br />

2011-12-07 17:00 Identifying indicators of illegal behaviour: carnivore<br />

killing in human-managed landscapes<br />

St. John, F.A.V.*, Bangor University; Keane, A.M., University<br />

College London; Edwards-Jones, G., Bangor University; Jones, L.,<br />

n/a; Yarnell, R.W., Nottingham Trent University; Jones, J.P.G.,<br />

Bangor University;<br />

Managing natural resources often depends upon influencing people’s<br />

behaviour. Effectively targeting interventions to discourage environmentally<br />

harmful behaviours is challenging because those involved may be unwilling<br />

to identify themselves. Non-sensitive indicators of sensitive behaviours<br />

are t<strong>here</strong><strong>for</strong>e needed. Previous studies have investigated people’s attitudes,<br />

assuming attitudes reflect behaviour. T<strong>here</strong> has also been interest in using<br />

psychological bias resulting from people’s tendency to imagine that others<br />

are more like themselves than they really are, to identify those involved in<br />

sensitive behaviours. However, t<strong>here</strong> has been little attempt to test the value<br />

of potential indicators. We use the randomised response technique, designed<br />

<strong>for</strong> investigating sensitive behaviours, to investigate potential indicators of<br />

human-wildlife conflict. We estimate the proportion of farmers in northeastern<br />

South Africa killing five carnivore species, and investigate indicators<br />

of carnivore killing using a modified logistic regression model. One-fifth<br />

of farmers admitted to killing leopards in the last year. Farmers’ attitudes<br />

towards carnivores and their estimates of their peers’ carnivore killing<br />

behaviour predict the likelihood of farmers killing carnivores. Attitude and<br />

bias in estimates of peer behaviour may be useful indicators of people’s<br />

involvement in illicit behaviours. Such in<strong>for</strong>mation can be used to identify<br />

groups of people to engage in behaviour-change interventions.<br />

2011-12-07 16:45 Can pocket parks support suburban birds in a<br />

compact city?<br />

Stagoll, K*, Fenner School of Environment and <strong>Society</strong>, Australian<br />

National University; Manning, AD, Fenner School of Environment<br />

and <strong>Society</strong>, Australian National University; Knight, E, Fenner<br />

School of Environment and <strong>Society</strong>, Australian National University;<br />

Fischer, J, Faculty of Sustainability, Leuphana University Lueneburg;<br />

Lindenmayer, DB, Fenner School of Environment and <strong>Society</strong>,<br />

Australian National University<br />

The desire to improve urban sustainability is motivating many city planners<br />

to adopt growth strategies that increase residential density, leading to<br />

substantial changes in the urban <strong>for</strong>m. In Australia, <strong>for</strong> example, Canberra<br />

is moving from a “garden city” approach of large residential blocks with<br />

extensive private open space, to a “compact city” plan of small blocks<br />

with high levels of impervious surface cover. What affect this change will<br />

have on biodiversity remains unclear, but it is expected that the role of<br />

public green space in providing wildlife habitat will become critical. In<br />

our study, we explored the role of suburban “pocket” parks as habitat <strong>for</strong><br />

birds, and how this role changes with different urban <strong>for</strong>ms. We looked<br />

at the effects of several scales, including the vegetation structure within<br />

the park, the amount of green space within the neighbourhood, and the<br />

housing structure of the suburb. We also considered the importance of<br />

physical connectivity between the park and other public green space. We<br />

conclude that pocket parks, especially those retaining large native trees, (1)<br />

provide <strong>for</strong>aging and nesting resources <strong>for</strong> a wide diversity of birds, (2) help<br />

maintain a continuum of stepping stones throughout suburban areas, and<br />

(3) may function as suburban refugia as cities become more compact.<br />

2011-12-07 10:30 <strong>Conservation</strong> translocations: from reintroduction<br />

to assisted colonisation.<br />

Stanley Price, MR, University of Ox<strong>for</strong>d; Seddon, P*, University of<br />

Otago; Moehrenschlager, A, Calgary Zoo<br />

Reintroductions have developed greatly over the last 40 years from,<br />

at worst, irresponsible releases to rigorously designed and monitored<br />

scientific practice. Quantitatively, reintroductions have increased both<br />

absolutely and in in the diversity of taxa reintroduced, t<strong>here</strong>by constituting<br />

a significant element in the conservation tool box. This presentation will<br />

briefly review the development of reintroduction science and practice,<br />

proposing a new typology <strong>for</strong> the array of translocations <strong>for</strong> conservation<br />

purposes. But, reintroduction science and practice must now prepare <strong>for</strong><br />

the challenges and opportunities af<strong>for</strong>ded by climate change and other<br />

major threats to species’ persistence. This presentation will explore the<br />

issues around future reintroductions and the proactive moving of species<br />

<strong>for</strong> conservation purposes – ‘assisted colonisation’. We will explore the<br />

potentials <strong>for</strong> reintroduction in the context of <strong>for</strong>thcoming major change<br />

in many contemporary communities and the prospect of novel climates<br />

and ecosystems; we will then outline the consequent novel considerations<br />

around policy, sociology and ethics, as well as the need to advance urgently<br />

our knowledge and capacity in diverse areas such as risk and decisionmaking,<br />

genetics and micro-evolution, priority-setting, reintroduction<br />

objectives and measures of success, and the requirement <strong>for</strong> climate models<br />

at appropriate scale <strong>for</strong> reintroductions.<br />

2011-12-07 18:15 Does research and conservation management reduce<br />

lifetime reproductive success in a long-lived seabird?<br />

STEIN, AM*, Zoology Department, University of Otago, PO Box 56<br />

Dunedin 9054; van Heezik, Y, Zoology Department, University of<br />

Otago, PO Box 56 Dunedin 9054; Seddon, PJ, Zoology Department,<br />

University of Otago, PO Box 56 Dunedin 9054;<br />

The analysis of long-term life history data can be used to calculate lifetime<br />

reproductive success. Individuals can vary greatly in productivity according<br />

to life history traits, and a relatively low proportion of individuals may<br />

actually contribute genetically to the next generation. It is common <strong>for</strong><br />

vulnerable or threatened species to be subject to consistent and high levels<br />

of disturbance <strong>for</strong> scientific studies and conservation ef<strong>for</strong>ts. These ef<strong>for</strong>ts<br />

often necessitate the handling of birds, eggs, and their young, or involve more<br />

intrusive activities such as blood sampling, stomach sampling and TDR<br />

deployment. It is often unknown what impact these activities may have on<br />

the species that such research is intending to benefit. The aim of this study<br />

is to determine which life history components, including interventions<br />

<strong>for</strong> scientific research and conservation management, influence lifetime<br />

reproductive success in yellow-eyed penguins (Megadyptes antipodes) on<br />

the Otago Peninsula, New Zealand. This will be achieved by analysing a<br />

long-term dataset of life history and breeding data recorded from individual<br />

birds.<br />

161

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