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44 results for “captive breeding”
Figure 1 in Breeding and reproductive behaviour of the neo-tropical opossum, Didelphis marsupialis insularis, Allen 1902 under captive conditions
Figure 1. Design and layout of Adult Units using a Single Corridor Layout. Source: Tardieu and Garcia, 2018).
Figure 2 in Breeding and reproductive behaviour of the neo-tropical opossum, Didelphis marsupialis insularis, Allen 1902 under captive conditions
Figure 2. Photo of opossum breeding unit showing – (A) Human Access panel to Male; (B) Male Cage; (C & D) Male Access panels to females; (E) Female Cage; (F) Human Access panel to Female.
Fig. 3 in Captive breeding program for Scinax alcatraz (Anura: Hylidae): introducing amphibian ex situ conservation in Brazil
Fig. 3. Breeding of Scinax alcatraz at São Paulo Zoo. a) A pair in amplexus. b) Eggs deposited in the water. c) Maintanance of tadpoles in plastic pots with filtered water. d) Post-metamorph individuals (SVL x=12.49 mm). Photos by Cybele Lisboa.
Fig. 6 in Captive breeding program for Scinax alcatraz (Anura: Hylidae): introducing amphibian ex situ conservation in Brazil
Fig. 6. Range of environmental conditions (relative humidity and air temperature) most favorable for reproduction of Scinax alcatraz in captivity.
Fig. 5 in Captive breeding program for Scinax alcatraz (Anura: Hylidae): introducing amphibian ex situ conservation in Brazil
Fig. 5. Correlation between breeding events of Scinax alcatraz and environmental conditions (a) relative humidity and (b) air temperature from August 2013 to December 2017. Pearson product-moment Correlation Coefficient: r = 0.323; p <0.001; N = 732.
Fig. 2 in Captive breeding program for Scinax alcatraz (Anura: Hylidae): introducing amphibian ex situ conservation in Brazil
Fig. 2. Laboratory colony of Scinax alcatraz at Sao Paulo Zoo. a) Aquariums for maintanance of juveniles and adults. b) Plastic cups with filtered water and submerged plants for refuge. Photos by Cybele Lisboa.
Figure 5 in Husbandry, captive breeding, larval development and stages of the Malayan horned frog Megophrys nasuta (Schlegel, 1858) (Amphibia: Anura: Megophryidae)
Figure 5. Megophrys nasuta larvae in stages 18 to 22; blue color is caused by the blue cellular material at the aquarium ground / background while taking photographs. Photos: R. Bach, T. Ziegler, D. Karbe.
Figure 2 in Husbandry, captive breeding, larval development and stages of the Malayan horned frog Megophrys nasuta (Schlegel, 1858) (Amphibia: Anura: Megophryidae)
Figure 2. Megophrys nasuta at the amphibian breeding unit at the Cologne Zoo a) calling male, b) couple in ampleXus during egg deposition, c) embryos, and d) hatched larvae with yolk sacs. Photos: D. Karbe, A. Heidrich, T. Ziegler.
Figure 1 in Husbandry, captive breeding, larval development and stages of the Malayan horned frog Megophrys nasuta (Schlegel, 1858) (Amphibia: Anura: Megophryidae)
Figure 1. Megophrys nasuta enclosures in the amphibian breeding unit at the Cologne Zoo: a) terrarium of the adults, b) rearing tank for larvae at early developmental stages, c) aquaria for advanced larval stages, and d) rearing terraria for juveniles. Photos: D. Karbe.
Figure 4 in Building capacity to implement conservation breeding programs for frogs in Madagascar: Results from year one of Mitsinjo's amphibian husbandry research and captive breeding facility
Figure 4. Seven species of frogs were included in a husbandry research and technician training program during the first year of the project. The IUCN Red List status, in parenthesis, follows species. A) Heterixalus betsileo (LC). B) Mantidactylus betsileanus, (LC). C) Heterixalus punctatus (LC). D) Blommersia blommersae (LC). E) Guibemantis aff. albolineatus "Andasibe" (DD). F) Stumpffia sp. "Ranomafana" (DD). G) Boophis pyrrhus (LC).
Figure 3 in Building capacity to implement conservation breeding programs for frogs in Madagascar: Results from year one of Mitsinjo's amphibian husbandry research and captive breeding facility
Figure 3. Terraria and aquaria at the breeding facility. A) Terraria setup on shelving and plumbed so wastewater flows into a drain in the floor. B) A terrarium housing a group of Boophis pyrrhus. C) Aquaria for raising tadpoles. D) Boophis pyrrhus tadpoles produced at the facility.
Figure 9 in Building capacity to implement conservation breeding programs for frogs in Madagascar: Results from year one of Mitsinjo's amphibian husbandry research and captive breeding facility
Figure 9. Pilot study and training exercise on the optimal larval diet for Mantidactylus betsileanus.
Figure 1. The facility was constructed between November 2010 and March 2011 in Building capacity to implement conservation breeding programs for frogs in Madagascar: Results from year one of Mitsinjo's amphibian husbandry research and captive breeding facility
Figure 1. The facility was constructed between November 2010 and March 2011 from the foundations of an old abandoned forest station. A) Original abandoned building in January 2009. B) Facility construction November 2010. C) Facility construction December 2010. D) Facility construction January 2011.
Figure 8 in Building capacity to implement conservation breeding programs for frogs in Madagascar: Results from year one of Mitsinjo's amphibian husbandry research and captive breeding facility
Figure 8. Locally-sourced crickets from Andasibe being bred at Mitsinjo's facility. A) Field cricket (Modicogryllus sp.). B) Large field cricket (Modicogryllus sp.). C) Large black cricket (Gryllus sp.). D) Tropical house cricket (Gryllodes sigillatus). E) Cave cricket (Rhaphidophoridae). F) Shelves with boxes housing field crickets and tropical house crickets.
Figure 2 in Building capacity to implement conservation breeding programs for frogs in Madagascar: Results from year one of Mitsinjo's amphibian husbandry research and captive breeding facility
Figure 2. Overview of the biosecure Mitsinjo amphibian captive breeding and husbandry research center as of April 2012.
Figure 5 in Building capacity to implement conservation breeding programs for frogs in Madagascar: Results from year one of Mitsinjo's amphibian husbandry research and captive breeding facility
Figure 5. Lectures and discussions during January-March 2011 helped train Mitsinjo technicians in captive frog husbandry techniques.
Figure 7. A in Building capacity to implement conservation breeding programs for frogs in Madagascar: Results from year one of Mitsinjo's amphibian husbandry research and captive breeding facility
Figure 7. A) Fruit fly cultures on shelves at the facility. B) Fruit flies are cultured in discarded plastic water bottles collected in Andasibe. Fabric is secured in place, over the top with rubber bands, and strips of plastic bag are placed inside (above the media) on which the flies can deposit eggs.
The genetic consequences of captive breeding, environmental change and human exploitation in the endangered peninsular pronghorn
<p>Binned microsatelite data of the peninsular pronghorn subspecies (Antilocapra americana peninsularis). Data is organized in by year manner. Each population correspond to the year samples were collected from, for example Pop_09 corresponds to samples collected from year 2009, whereas Pop_21 corresponds to the samples collected from year 2021.</p> <p> </p>
Microsatellite genotypes for temporal monitoring of the Floreana Island Galapagos Giant Tortoise captive breeding program
<p><span>Captive breeding programs benefit from genetic analyses that identify relatedness between individuals, assign parentage to offspring, and track levels of genetic diversity. Monitoring these parameters across breeding cycles is critical to the success of a captive breeding program as it allows conservation managers to iteratively evaluate and adjust program structure. However, in practice, genetic tracking of breeding outcomes is rarely conducted. Here, we examined the first three offspring cohorts (2017 – 2020) of the genetically-informed captive breeding program for the Floreana Island Galapagos giant tortoise, </span><em><span>Chelonoidis niger</span></em><span>. This captive breeding program is unique as the Floreana tortoise has been extinct since the 1800s, but its genome </span><span>persists, in part, in the form of living hybrids with the extant Volcano Wolf tortoise, <em>Chelonoidis becki</em>. Breeding over the study period took place at the Galapagos National Park Directorate breeding facility in four corrals, each containing three females and two males. Using 17 microsatellite markers, we were able to assign parentage to 94 of the 98 offspring produced over the study period. </span><span>We observe that despite the addition of more founders since the pilot breeding program, the effective population size remains low, and changes to the arrangements of breeding corrals may be necessary to encourage more equal reproductive output from the males. </span><span>This study demonstrates the value of hybrids for species restoration and the importance of continually reassessing the outcomes of captive breeding. </span></p>
Figure 3 in Breeding and reproductive behaviour of the neo-tropical opossum, Didelphis marsupialis insularis, Allen 1902 under captive conditions
Figure 3. Photo of opossum breeding unit showing view from top of enclosure.
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