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Aldama, J. J. and Delibes, M. 1990.
Some preliniary results on rabbit energy utilization by the Spanish lynx. Acta
Vertebrata Doñana 17(1): 116-121.
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The lynx digestion efficiency
fed with rabbits was examined following the additive energetics model discussed
by Grodzinski and Wunder (1975). The main objective of this work was to
determine the metabolizable energy obtained by lynxes from wild rabbits. It was
estimated: 1) the fresh biomass that the lynx did not use from each killed
rabbit, 2) the gross energy intake of the consumed biomass, 3) the energy lost
in faeces and consequently the digested energy, and 4) finally, the
metabolizable energy.
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Aldama_&_Delibes_1990_Rabbit_energy_utilization_by_Spanish_lynx.pdf
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Aldama, J. J. and Delibes, M. 1991.
Observations of feeding groups in the Spanish lynx (Felis pardina) in the
Donana National Park, SW Spain. Mammalia 55(1): 143-147.
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Usually lynxes forage alone.
However, the low rate of interactions with conspecifics probably does not mean
a reduction of the ability of each lynx to recognize other individuals. For
this reason, in some particular cases family-related groups may gather as it
happens with some more social species of felids, such as lions. Herein we
report two observations (one year elapsed) of a family related feeding group of
free-ranging radiocollared Spanish lynxes at Doñana region, SW Spain. The
family group was formed by an adult female, mother of a young independent
female and a yearling male.
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Aldama_&_Delibes_1991_Feeding_groups_in_Spanish_lynx.pdf
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Aldama, J. J. and Delibes, M. 1991.
Field observations of Spanish lynxes (Felis pardina) playing with prey in
Donana, south-west Spain. J. Zool. ,Lond. 225: 683-684.
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Play behaviour is well
documented in felids, but the funcional significance of this activity remains
unclear. Moreover, most of the information conserning play in felids has been
provided by observations of domestic and/or captive individuals as free-living
wild felids are usually rare, solitary and frequently nocturnal. In this note
we report some observations of two free-living Spanish lynxes (Felis pardina),
a juvenile and an adult, playing with wild rabbits (Oryctolagus cuniculus)
in Doñana, south-west Spain.
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Aldama_&_Delibes_1991_Spanish_lynx_playing_with_prey.pdf
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Aldama, J. J., Beltran, J. F.,
and Delibes, M. 1991. Energy expenditure and prey requirements of
free-ranging Iberian lynx in Southwestern Spain. J. Wildl. Manage. 55(4):
635-641.
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We developed an additive model
to estimate seasonal energy expenditure of nonreproductive, free-ranging
Iberian lynx (Felis pardina) at Doñana National Park in southwestern
Spain. We considered only resting, locomotion, hunting, and eating costs. Data
for the model were provided by radiomonitoring an adult male (15.4 kg) and an
adult female (9.95 kg) in 24-hour samples (n=53) between 1983 and 1985. Average
daily energy expenditure was 912 kcal for the male and 673 kcal for the female,
with greater seasonal variation in the male. Based on the energy content fo the
lynx's staple prey, the European rabbit (Oryctolagus cuniculus), we
estimated the prey requirements of this endangered felid as about 1 rabbit per
day.
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Aldama_et_al_1991_Energy_and_prey_of_Iberian_lynx.pdf
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Alfonso, C. 2002. Esperanza con futuro. ambienta, Febrero
2002: 29-34.
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Popular article on the Iberian Lynx Captive
Breeding Programme that has recently been established, and which has the
fundamental objective to secure the conservation of this big cat.
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Alfonso_2002_Esperanza_con_futuro.pdf
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Alfonso, C. 2003. Un paso definitivo. ambienta, Julio-Agosto 2003: 8-15.
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The Ministry of
Environment and the Junta de Andalucía have signed a Agreement to apply the
National Strategy for the Conservation of the Iberian Lynx in Andalucía. It
directs to increase the efforts for the development of a unique coordinated
programme for the conservation of the lynx in Andalucía through the impulse of
the Captive Breeding Plan, the amelioration of lynx habitat, the recovery
of the rabbit populations, the elimination of the non-natural mortality and the
surveillance of the populations. |
Alfonso_2003_Un_paso_definitivo.pdf
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Angulo, E. 2001. When DNA research menaces diversity. Nature 410:
739.
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I would like to give an example where genetic engineering of
viruses can undermine careful management of natural resources. Two new rabbit
virus strains are being developed for opposing reasons. On the one hand, a
group in Australia is modifying rabbit myxoma virus to transmit reproductive sterility
and so reduce numbers in a region where rabbits constitute a pest. On the
other, a European group is modifying myxoma virus to express rabbit
haemorrhagic disease virus capsid protein to protect rabbits against both
diseases and encourage the recovery of wild populations within the species'
original distribution area.
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Angulo_2001_When_DNA_research_menaces_diversity.pdf
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Angulo, E. and Villafuerte, R.
2003. Modelling hunting strategies for the conservation of wild rabbit
populations. Biological Conservation 115: 291-301. |
Recently, European wild rabbit (Oryctolagus
cuniculus) populations have undergone a sharp decline that may be exacerbated
by hunting. We investigate the effects of the timing of hunting on the
conservation of wild rabbit using a model for rabbit population dynamics.
Scenarios with different hunting rates and age strategies were simulated for
different population qualities. We interviewed hunters to ascertain the degree
to which they would accept a change in the timing of hunting. We also
investigated the hunting pressure applied by hunters and its relationship with
rabbit abundance. Modelling results indicate that the current hunting season
has the greatest impact on rabbit abundance. Hunting in late spring optimises
hunting extraction while conserving rabbit populations. When the rabbit
population quality is low the effects of age strategies and the timing of
hunting are less important than the effect of the hunting rate applied. Almost
half the hunters would agree to policy changes. More than 75% of hunters
implemented self-imposed hunting restrictions to improve rabbit populations,
that were more frequently applied in high rabbit abundance areas. Therefore,
changing the timing of hunting and increasing the participation of hunters in
low abundance areas could optimise both the exploitation and the conservation
of wild rabbit populations in southwestern Europe.
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Angulo_&_Villafuerte_2003_Modelling_hunting_strategies_for_rabbit_populations.pdf
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Anonymous. 1978. Spanish or Pardel lynx. Unpublished work.
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Basic information on Iberian
lynx distribution, population size, habitat and ecology, threats to survival,
conservation measures taken, and conservation measures proposed.
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Anonymous_1978_Datasheet_Spanish_or_Pardel_lynx.pdf
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Aparicio, J. P., Solari, H. G., and Bonino, N.
2004. Competition and coexistence in host-parasite
systems: the myxomatosis case. Popul. Ecol. 46: 71-85.
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Co-circulation of several
strains of parasites has been observed in many host-parasite systems. However,
simple epidemiological models cannot sustain this coexistence. In this work we
study the coexistence of viral strains in the myxomatosis case. Myxomatosis, a highly lethal disease of
the European rabbit, has been used in Australia and Europe as a biological
control of rabbit populations. A few years after its introduction, the original
highly virulent strains were almost completely replaced by field strains
covering a wide range of virulence. Here, we study several mechanisms that may
explain the field observations. First we considered spatial heterogeneity. The
establishment of any strain over regions occupied by host populations may delay
the spread of any superior competitive virus strain, producing global
coexistence in the long term. On the other hand, sub-populations with different
resistance levels in epidemiological contact, as observed in the field, can
maintain several different virus strains co-circulating. The second class of
mechanism introduces diversity among hosts of a local population sharing a
territory. We considered different classes of host resistance to myxomatosis:
belonging to a resistance class is a random fact. Host age-dependent resistance
is also especially considered. These types of population heterogeneity can
sustain local coexistence for many years, although exclusion takes place for
long enough periods. The concurrent action of both types of mechanisms could
explain why the diversity of virus strains is sustained, and the local
coexistence. Finally, we briefly discuss the influence of host genetic dynamics
in the coevolution of the system.
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Aparicio_et_al_2004_Host-parasite_systems_-_the_myxomatosis_case.pdf
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Araújo, M. B. 1999. Distribution patterns of
biodiversity and the design of a representative reserve network in Portugal.
Diversity and Distributions 5: 151-163.
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Representativeness is a desirable property of
conservation networks. In this paper an attempt is made to assess the
efficiency of current conservation networks in Portugal in representing
vertebrates (reptiles and amphibians) and plants (gymnosperms, pteridophytes
and bryophytes). It was found that whilst the protected areas do not sample all
species in the database they provide a better result than choosing areas at
random. For the goal of maximizing representation of taxa per unit area
hotspots and complementarity performed better. A pattern of over-representation
of vertebrates in relation to lower plant was discovered among selected
conservaiton areas in Portugal suggesting that charismatic organisms with large
home ranges may not always be the most appropriate surrogates for biodiversity
when representativeness is sought. When trying to fill the gaps in current
protected areas with additional areas only complementarity preformed better
than choosing areas at random. Both rarity and richness hotspots gave worse results.
Opportunistic administrative criteria such as supplementing the PAS with other
conservation areas (CORINE Biotopes) without taking into account their
contribution to a representation goal was nearly half as good as choosing areas
at random. The results recall for the need of explicit goals and accountable
methods in area selection fro conservation and reinforce the role of
complementarity for finding additional areas to protected areas when limited
resources are available for "in situ" conservation.
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Araujo_1999_Biodiversity_distribution_and_reserve_network_design_in_Portugal.pdf
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Aymerich, M. 1982. Etude comparative des régimes alimentaires du lynx
pardelle (Lynx pardina Temminck, 1824) et du chat sauvage (Felis silvestris
Schreber, 1777) au centre de la péninsula Ibérique. Mammalia
46(4): 515-521.
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A comparative study of the feeding habits of the Spanish lynx and
the wildcat was conducted in central Spain, by analyzing digestive tracts of
these 2 spp. Rabbits, hares and red partridges amount to 97.2% for the lynx and
79.3% for the cat of the biomass consumed. The only main difference is the
larger number of small mammals caught by the cat. The similitary of their feeding
habits and the fact that they live in the
same biotope indicate a possible feeding rivalry between these 2
felines; this competition does not seem to be important for the cat's survival
at a regional level. It could be possible that locally, lynx has a negative influence on the cats density;
this fact has not been demostrated.
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Aymerich_1982_Regimes_alimentaires_du_lynx_pardelle_et_du_chat_sauvage.pdf
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