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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 />

2011-12-07 15:30 The Yellowstone to Yukon <strong>Conservation</strong> Initiative:<br />

Continental scale collaboration <strong>for</strong> biodiversity conservation<br />

Francis, WL*, Yellowstone to Yukon <strong>Conservation</strong> Initiative;<br />

The ranges of large mammals that once occupied much of North America<br />

are now limited to the mountainous west of the continent. Even within<br />

that landscape, transportation networks, subdivision, resource exploration<br />

and development and increasing human incursions into remote areas<br />

are fragmenting habitats and populations, threatening the persistence of<br />

sensitive species. The impacts of climate change will be exacerbated by<br />

habitat fragmentation. The Yellowstone to Yukon <strong>Conservation</strong> Initiative<br />

(Y2Y) is a response to these threats, offering an inspiring vision of landscape<br />

connectivity at the continental scale. The Cabinet-Purcell Mountain<br />

Corridor (CPMC) Project will be presented as an example of successful<br />

trans-boundary conservation collaboration. Using grizzly bears as the focus<br />

of conservation planning, the CPMC Project is creating the conditions that<br />

will enable large mammal populations in southeastern British Columbia,<br />

northern Idaho and western Montana to stay connected to each other and<br />

to move in response to changing habitat conditions.<br />

2011-12-08 12:15 Reproductive technologies to help recovery of<br />

threatened New Zealand vertebrates <strong>for</strong> ecological restoration<br />

Frank Molinia*, Landcare Research, Private Bag 92170, Auckland<br />

1142, New Zealand; Dianne Gleeson, Landcare Research, Private<br />

Bag 92170, Auckland 1142, New Zealand; Edward Narayan,<br />

Environmental Futures Centre, School of Environment, Gold Coast<br />

Campus, Queensland 4222, Australia; Jennifer Germano, San<br />

Diego Zoo Institute <strong>for</strong> <strong>Conservation</strong> Research, 15600 San Pasqual<br />

Valley Road, Escondido, Cali<strong>for</strong>nia 92027, USA; Alison Cree, Phil<br />

Bishop, Department of Zoology, University of Otago, PO Box 56,<br />

Dunedin 9054, New Zealand; Richard Jakob-Hoff, New Zealand<br />

Centre <strong>for</strong> <strong>Conservation</strong> Medicine, Auckland Zoo, Private Bag, Grey<br />

Lynn, Auckland 1245, New Zealand; John Cockrem, Institute of<br />

Veterinary, Animal and Biomedical Sciences, Massey University,<br />

Private Bag 11222, Manawatu Mail Centre, Palmerston North<br />

4442, New Zealand; Neil Gemmell, Centre <strong>for</strong> Reproduction and<br />

Genomics, Invermay Agricultural Centre, Puddle Alley, Private Bag<br />

50034, Mosgiel 9053, New Zealand<br />

Reproductive technologies are valuable tools <strong>for</strong> understanding speciesspecific<br />

reproductive mechanisms. Modern techniques have been used <strong>for</strong><br />

managing wildlife ex situ and in recent years have even contributed to in<br />

situ conservation. In New Zealand a suite of reproductive technologies are<br />

in development to recover threatened species as key elements of ecological<br />

restoration. Protocols established in model species are being adapted <strong>for</strong> use<br />

in target threatened vertebrates (e.g. Leiopelmatid frogs, Grand and Otago<br />

skinks and Blue duck) in three stages over time. The first stage involves<br />

assessment of reproductive function, status and welfare using urinary/faecal<br />

metabolite measures to non-invasively sex individuals and/or monitor<br />

the hormones of reproduction and stress. Routine sperm collection and<br />

assessment will also be used to confirm the identity of males and to detect<br />

problems with sperm quality. These procedures underpin the second stage<br />

which is development of assisted breeding techniques like liquid- and<br />

frozen-storage of sperm and artificial insemination/fertilisation. The final<br />

stage is to establish genetic resource banks of germplasm as a valuable<br />

bet-hedging strategy to safeguard species-level genetic variation. These<br />

techniques will increase our knowledge of native species reproduction and<br />

offer much promise as tools to enhance the production of offspring of<br />

desired genetic make-up <strong>for</strong> in situ recovery and secure genetic repositories<br />

<strong>for</strong> future restoration needs.<br />

2011-12-09 17:00 The long and the short of it; historic and<br />

contemporary genetic structure of an endangered Australian marsupial,<br />

the long-nosed potoroo (Potorous tridactylus)<br />

Frankham, GJ*, Department of Zoology, University of Melbourne,<br />

Victoria, 3010; Handasyde, KA, Department of Zoology, University<br />

of Melbourne, Victoria, 3010; Eldridge, MDB, Evolutionary <strong>Biology</strong><br />

Unit, Australian Museum, Sydney, NSW 2010;<br />

The long-nosed potoroo (Potorous tridactylus), one of the smallest members<br />

of the marsupial superfamily Macropodoidea, is currently restricted to<br />

disjunct populations throughout coastal south-eastern Australia, from<br />

southern Queensland to western Victoria and Tasmania. It is listed as<br />

‘vulnerable’ under the national Australian Environment Protection and<br />

Biodiversity <strong>Conservation</strong> Act 1999. Understanding both the historic and<br />

contemporary genetic structure of fragmented populations is important<br />

<strong>for</strong> effective conservation and to protect evolutionary potential. However,<br />

the long-nosed potoroo’s elusive nature has limited investigations to date.<br />

My study has investigated broad-scale phylogeographic patterning across<br />

the species range, using mitochondrial DNA (mtDNA) and nuclear DNA<br />

(nuDNA) sequence analysis. Tissue samples were collected (n = >500) from<br />

throughout the species range. MtDNA (control region, ND2 and CO1)<br />

sequence analysis identified three previously unrecognised and significantly<br />

divergent lineages, corresponding to distinct geographic regions. However,<br />

analysis of nuDNA (BRCA, Rag, ApoB) sequences, did not show the same<br />

structuring, highlighting the importance of investigating both genomes <strong>for</strong><br />

a complete understanding of evolutionary and population history. A fine<br />

scale mtDNA control region and microsatellite analysis is also underway<br />

to enable the most appropriate geographic scale <strong>for</strong> local population<br />

management to be determined.<br />

2011-12-09 14:45 Predicting the risk of outbreeding depression:<br />

critical in<strong>for</strong>mation <strong>for</strong> managing fragmented populations<br />

FRANKHAM, R*, Macquarie University, NSW 2109, Australia;<br />

Ballou, JD, Smithsonian <strong>Conservation</strong> <strong>Biology</strong> Institute, Washington,<br />

DC 2008, USA; Eldridge, MDB, Australian Museum, 6 College St,<br />

Sydney, NSW 2010 Australia; Lacy, RC, Chicago Zoological <strong>Society</strong>,<br />

Brookfield, IL60513, USA; Ralls, K, Smithsonian <strong>Conservation</strong><br />

<strong>Biology</strong> Institute, Washington, DC 2008, USA; Dudash, MR,<br />

University of Maryland, College Park MD20742, USA; Fenster, CB,<br />

University of Maryland, College Park MD20742, USA;<br />

Many small isolated population fragments would likely benefit from reestablishment<br />

of gene flow from other fragments to recover reproductive<br />

fitness and genetic diversity, but managers rarely do this due partly to<br />

fears of outbreeding depression (OD). Rapid development of OD is due<br />

primarily to adaptive differentiation or fixation of chromosomal variants.<br />

Fixed chromosomal variants can be detected empirically. Using the breeders’<br />

equation, we predicted that the risk of OD due to adaptive differentiation<br />

is a function of selection, genetic diversity, effective population sizes,<br />

and generations of isolation. Empirical data indicated that populations<br />

in similar environments had not developed OD even after thousands of<br />

generations of isolation. We devised a decision tree <strong>for</strong> practitioners to<br />

predict the risk of OD. The risk of OD in crosses between populations is<br />

elevated when they have at least one of the following: are distinct species,<br />

have fixed chromosomal differences, exchanged no genes in the last 500<br />

years, or inhabit different environments. Conversely, the risk of OD in<br />

crosses between two populations of the same species is low <strong>for</strong> populations<br />

with the same karyotype, isolated <strong>for</strong>

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