Society for Conservation Biology: 2002 Annual Meeting
Abstracts
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Society for Conservation Biology: 2002 Annual Meeting
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Society for Conservation Biology 16th
Annual Meeting July 14-July 19 2002
co-hosted by DICE and the British Ecological Society
Abstracts for Conservation Genetics
Session One
Monday 15th July, 10.15 - 12.15, Rutherford
Lecture Theatre 1
Chair: Colin Hughes
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(BLOCK CAPITALS indicate the presenting author)
10.15 - 10.30
RIDLEY, JO and Jan Komdeur. Centre for Ecology Evolution and Conservation, School
of Biological Sciences, UEA, Norwich, Norfolk NR15 1DD, UK, <j.ridley@uea.ac.uk>
(JR), University of Groningen, Netherlands (JK).
GENES OR POPULATIONS? A CONCILIATORY APPROACH TO SPECIES MANAGEMENT
To incorporate genetic priorities into the management of endangered species, we need
to understand the relative risks that genetic threats pose, and also to be able to
identify strategies that place appropriate emphasis on these risks. Using a behaviour-based
population model of the Seychelles warbler, a general method for deriving population
genetic data from any individual-based population model is demonstrated. This allows
us to estimate the effective population size on the island of Cousin to be 45, in
comparison to a population size of 320. For almost any mutation rate estimate this
effective population size will not be viable in the medium term. The major reason
for the relatively small effective population size is spatial variation in fitness,
something that many reserve-based management plans will tend to exacerbate. As habitat
usage in the Seychelles warbler model is based on individuals’ attempts to maximise
fitness, the effects of habitat manipulation on both carrying capacity and effective
population size can be predicted. Whilst management practices can favour population
size or effective population size, this approach allows general predictions to be
made as to how to manage in order to benefit both.
10.30 - 10.45
HUGHES, COLIN R., Steven R. Beissinger, and Rebecca R. Melland. University of
Miami, Box 249118, Coral Gables, FL, 33124, USA, <hughes@fig.cox.miami.edu>
(CRH), University of California Berkeley, CA 94720, USA (SRB), and University of
North Dakota, Grand Forks, ND, 58202, USA (RRM).
THE SCALE OF GENETIC POPULATION STRUCTURING IN A NEOTROPICAL SAVANNAH-DWELLING PARROT.
The geographic scale of demographic and genetic processes are poorly known for tropical
birds. On a ranch in the Llanos of Venezuela, individually marked Green-rumped parrotlets,
Forpus passerinus, are rarely resighted moving between two areas of savannah
separated by 1km of forest. However, many recruits into the breeding population are
immigrants. We collected blood samples from adults at the ranch, and 5 other locations
in Guárico, then genotyped individuals at 10 polymorphic microsatellite loci.
Analyses confirm that individuals disperse widely. First, females mate with extra-pair
males which are nesting over 1 km from the female’s own nest. The program CERVUS
was used to identify extra-pair mates and 14 of 64 extra-pair fertilisations were
shown to be with males living in the other savannah area. Second, we detected no
geographic population differentiation. Genepop and Arlequin were used to analyse
data from 7 loci for which the step-wise mutation model fit allele sizes. Pairwise
differentiation estimates between the ranch and the most distant population sampled,
110 km south, were FST 0.000, RST = -0.005, neither significantly different from
zero. There was no indication of isolation by distance, (Mantel test P>.05).
Our results show that this open-country bird has an open population structure.
10.45 - 11.00
SWANSON, BRADLEY J. Department of Biology. Central Michigan University, Mount
Pleasant, MI 48859, USA, <brad.swanson@cmich.edu>.
THE ROLE OF HABITAT FRAGMENTATION IN THE EROSION OF GENETIC DIVERSTIY IN LEK BREEDING
GROUSE
Every species of lekking bird in the United States has at least one threatened population
experiencing rapid population declines, possibly due to habitat loss, fragmentation,
or genetic decay. Lekking species lose genetic variation rapidly because of the large
variation in male reproductive success. I evaluated the amount of genetic variation
at 6 microsatellites in populations of sharptailed grouse, Tympanuchus phasianellu,
ranging in size from small isolated populations to large continuous populations.
This allowed me to evaluate the effect of habitat fragmentation and reduced population
size on genetic variation while controlling for the lek breeding system. Isolated
leks had significantly lower heterozygosity and number of alleles than leks of similar
size in continuous populations. The reduced genetic variation found in the isolated
leks indicates that habitat fragmentation is accelerating the rate of loss of genetic
variation. I also found an inverse relationship between the number of misassigned
genotypes and distance to the nearest neighbour lek indicating that dispersal between
leks can be a major source of genetic variation. These results suggest that translocation
of birds between leks can help to reduce genetic decay and the problems associated
with low levels of genetic variation.
11.00 - 11.15
GAUTSCHI BARBARA, Jürg-Paul Müller, Bernhard Schmid and Jacqui Shykoff.
Institut für Umweltwissenschaften, Universität Zürich-Irchel, Winterthurerstrasse
190, CH-8057 Zürich, Switzerland, <babagaut@uwinst.unizh.ch> (BG, BS),
Bündner Natur-Museum, Masanserstrasse 31, CH-7000 Chur, Switzerland (JPM) and
Laboratoire d'Evolution et Systématique, CNRS UPRESA 8079, Université
Paris-Sud, Bâtiment 362, 91405 Orsay Cedex, France (JS).
PAST POPULATION STRUCTURE OF THE BEARDED VULTURE IN EUROPE-A GENETIC TIME TRAVEL
Historical patterns of genetic structure and gene flow are key parameters in reintroduction
projects. Based on microsatellite data derived from museum specimens we reconstructed
the past population structure of the bearded vulture and determined the amount
of gene flow among seven European populations of the 19th century. We found a significant
genetic differentiation (FST = 0.131) with a significant effect of geographic
distance. Past migration rates between any of the European populations were 0.94
individuals per generation (private-allele-method). Currently, captive-bred bearded
vultures are being released in the Alps to re-establish the population that became
extinct in the early 1900s. Our data suggest that gene flow between the released
birds in the Alps and the extant natural populations in Europe is very likely. In
addition, a comparison between the original population of the Alps with the founders
of the captive population revealed a significant genetic difference between the two.
Thus gene flow between the newly established population and extant natural populations
may affect their genetic properties. Both may profit from a larger effective population
size, and genetic variation in genetically impoverished populations may be replenished.
On the other hand, locally disadvantageous alleles may be transferred increasing
the risk of outbreeding depression.
11.15 - 11.30
KRETZMANN, MARIA, Nieves Capote, José Antonio Godoy , José Antonio
Donázar and Juan José Negro. Natural Sciences Division, Southampton
College, Long Island University, Southampton, NY, 11968, USA, <mkretzmann@southampton.liu.edu>
(MK),
Department of Applied Biology, Estación Biológica de Doñana,
CSIC, Avenida de Maria Luisa s/n, 41013 Sevilla, Spain (NC, JAG, JAD, JJN).
GENETICALLY DISTINCT ISLAND POPULATIONS OF THE EGYPTIAN VULTURE (NEOPHRON PERCNOPTERUS)
The Egyptian vulture is a species in decline throughout Europe, with the largest
remaining breeding populations found in northern Spain. Iberian Peninsula populations
(~1200 pairs) migrate to Africa in winter, while small populations in the Canary
and Balearic Islands are apparently sedentary. We found that Egyptian vultures from
both of these island groups were significantly differentiated from Peninsula populations
(RST = 0.065-0.129, p = 0.000-0.007), using nine microsatellite loci isolated
in the related bearded vulture. Maximum genetic differentiation was observed between
the two island groups (RST = 0.279, p = 0.000). These island populations were
more distinct from mainland groups than was a small sample of a well-defined separate
subspecies from India (RST = 0.083-0.091, p = 0.023-0.024). In contrast, populations
within the Peninsula were not differentiated from one another at these microsatellite
loci (RST = -0.004-0.007, p = 0.442-0.675). Introductions of Egyptian vultures
from the larger northern breeding groups might therefore be appropriate in southern
Spain, but mainland birds should not be introduced to the islands if the genetic
distinctiveness of these groups is to be preserved. Independent conservation plans
are urgently required to protect these two island populations from extinction.
11.30 - 11.45
RUSSELLO, MICHAEL, Kevin Willis and George Amato. Center for Environmental Research
and Conservation, Columbia University, New York, NY, USA <russello@amnh.org>
(MR, GA), Wildlife Conservation Society, Science Resource Center, Bronx, NY, USA
(MR, GA), Minnesota Zoo, Apple Valley, MN, USA (KW).
EX SITU MANAGEMENT IN THE ABSENCE OF PEDIGREE INFORMATION:
A CONSERVATION GENETIC STRATEGY FOR THE ST. VINCENT AMAZON PARROT USING NOVEL GENETIC
MARKERS
The St. Vincent Amazon parrot, Amazona guildingii, is an endangered island
endemic species of particular conservation concern. A large captive population was
established on St. Vincent in the early 1980’s consisting of wild-caught birds of
unknown ancestry held previously by private citizens throughout the island. If properly
managed, this ex situ population could play a significant conservation role
as a source of individuals for population reinforcement and reintroduction. However,
population management has been hindered by a lack of pedigree information, preventing
the use of conventional pedigree-based management tools. Rather than employing the
common assumption of all founders equally unrelated and equally inbred, 8 microsatellite
loci were used to genotype the captive population (n=73) to estimate the underlying
relatedness structure. The costs associated with incorrectly assigning individuals
to relatedness categories based on a limited set of molecular markers precluded the
direct input of empirically derived relatedness values within the current suite of
population management tools. As a result, a new methodology was employed to incorporate
the genotypic data into a management strategy based on minimising mean kinship. This
analysis provided a specific set of breeding recommendations for a previously unmanaged
population and allowed for a rigorous evaluation of genetic and demographic goals.
11.45 - 12.00
PEREZ-SWEENEY, BEATRIZ, Claudio Valladares-Padua, and Don J. Melnick. Department
of Anthropology, Columbia University, New York, NY 10027, USA, <bmp8@columbia.edu>
(BP), Instituto de Pesquisas Ecologicas, C. Postal 47, 12960-000 Nazare Paulista,
Sao Paulo, Brazil (CVP), Center for Environmental Research and Conservation, Columbia
University, New York, NY 10027, USA (DJM).
USING GENETICS FOR BLACK LION TAMARIN (LEONTOPITHECUS CHRYSOPYGUS) METAPOPULATION
MANAGEMENT
Black lion tamarins (BLTs), limited to only eight forest fragments, are a critically
endangered flagship species in the Atlantic Forest of the Interior, São Paulo,
Brazil. To conserve this species, a metapopulation management plan involving translocations
is being developed. One of the objectives of this plan is the long-term conservation
of BLT genetic diversity. However, initially, it was not clear how genetically diverse
these monkeys were because previous studies uncovered little or no variation. We
performed a more detailed study of BLT population genetics by collecting samples
from six of eight populated forest fragments and assessing the level and distribution
of variation at autosomal microsatellite and mitochondrial DNA loci. These data indicate
considerable genetic diversity among BLTs, which should be incorporated into management
decisions for this species. In addition, the data suggest that: 1) future discovery
of BLT populations in unexplored forests will likely add to the overall genetic diversity
of the species; 2) that plans for translocating females should differ from those
of males; and 3) the degree of genetic relatedness among populations in different
forest fragments should inform the rate and pattern of translocations from one populated
fragment to another, as well as to uninhabited fragments.
12.00 - 12.15
FIRESTONE KAREN and Don Colgan
Evolutionary Biology Unit, Australian Museum, 6 College Street, Sydney, NSW 2010,
Australia
(karenf@austmus.gov.au)
ANCIENT DNA AND THE THYLACINE: CONSERVATION ISSUES IN THE CLONING DEBATE
The thylacine or Tasmanian tiger (Thylacinus cynocephalus) was the largest
extant carnivorous marsupial in Australia at the time of European settlement. The
species, the last representative of its family, went extinct on September 7, 1936
after less than 100 years of direct persecution by Europeans and a protracted decline
over 4000 years following the introduction and expansion of dingoes from Asia. The
blunt extermination of this species represents a nadir in the human experience of
the 20th century. The Australian Museum’s Thylacine Project, which ambitiously aims
to clone a living thylacine, has been a hotly debated and controversial topic among
the scientific and conservation communities but has captured the public’s imagination
since its inception in 1999. The science behind the project focusses on the use of
ancient DNA in molecular methodologies with the initial, and theoretically achievable,
goal of making genetic libraries encompassing the entire genome. Difficult ethical,
moral, and environmental issues need to be broached and huge technological hurdles
in molecular, cellular, and reproductive techniques need to be overcome if the ultimate
goal is to be feasible, not least of which is determining how the (conservatively)
estimated seventeen million fragments of DNA fit together to encode for a thylacine.
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