Abstract:Amphibians and reptiles are highly threatened vertebrate taxa with large numbers of species threatened with extinction. With so many species at risk, conservation requires the efficient and cost-effective application of all the tools available so that as many species as possible are assisted. Biobanking of genetic material in genetic resource banks (GRBs) in combination with assisted reproductive technologies (ARTs) to retrieve live animals from stored materials are two powerful, complementary tools in the con… Show more
“…Historically, GRBs have focused on cryopreserved gametes, and more specifically primarily sperm, reflecting the early development of artificial insemination in domestic animals and humans, which has provided models for many of their wild cousins. Recently, newer technologies such as somatic cell nuclear transfer (Iqbal et al, 2021) and induced pluripotent stem cells (Hildebrandt et al, 2021; Korody et al, 2021) are expanding roles for somatic cells in GRBs (Clulow et al, 2022; Praxedes et al, 2018; Ryder & Onuma, 2018). These technologies are not yet developed and tested for most species of conservation concern; as they become more widely available and used, customized guidelines for optimally using such GRBs to advance population management should be developed.…”
Genome resource banks (GRBs) have the potential to preserve the genetic diversity of a species over time, yet they are rarely utilized as effective components of conservation breeding programs. Advances have been made in reproductive biology, collection and storage techniques, and use of stored gametes for achieving successful reproduction, but there are few guidelines for integrating GRBs into established breeding programs. Here we present basic guidelines, focusing on strategies for the collection, maintenance, and use of semen GRBs for protecting genetic diversity. These guidelines should be applied in the context of the specific purposes and roles of a breeding program's GRB, which will differ among species depending on vulnerability to loss and the status of rescue and conservation efforts.We recommend establishing up to three types of collections: (1) a National Reserve to preserve a species' genetic diversity, to be used only as a last resort; (2) a Savings Account to be used periodically to invigorate a genetically depauperate population; and (3) a Checking Account to be used as a regular part of the breeding program. We present methods for identifying donors to maximize genetic diversity in a GRB, as well as strategies for maintaining and optimally using GRBs.
“…Historically, GRBs have focused on cryopreserved gametes, and more specifically primarily sperm, reflecting the early development of artificial insemination in domestic animals and humans, which has provided models for many of their wild cousins. Recently, newer technologies such as somatic cell nuclear transfer (Iqbal et al, 2021) and induced pluripotent stem cells (Hildebrandt et al, 2021; Korody et al, 2021) are expanding roles for somatic cells in GRBs (Clulow et al, 2022; Praxedes et al, 2018; Ryder & Onuma, 2018). These technologies are not yet developed and tested for most species of conservation concern; as they become more widely available and used, customized guidelines for optimally using such GRBs to advance population management should be developed.…”
Genome resource banks (GRBs) have the potential to preserve the genetic diversity of a species over time, yet they are rarely utilized as effective components of conservation breeding programs. Advances have been made in reproductive biology, collection and storage techniques, and use of stored gametes for achieving successful reproduction, but there are few guidelines for integrating GRBs into established breeding programs. Here we present basic guidelines, focusing on strategies for the collection, maintenance, and use of semen GRBs for protecting genetic diversity. These guidelines should be applied in the context of the specific purposes and roles of a breeding program's GRB, which will differ among species depending on vulnerability to loss and the status of rescue and conservation efforts.We recommend establishing up to three types of collections: (1) a National Reserve to preserve a species' genetic diversity, to be used only as a last resort; (2) a Savings Account to be used periodically to invigorate a genetically depauperate population; and (3) a Checking Account to be used as a regular part of the breeding program. We present methods for identifying donors to maximize genetic diversity in a GRB, as well as strategies for maintaining and optimally using GRBs.
“…If the goal is to capture genetic diversity from small populations, then assisted reproductive technologies, including hormonally induced gamete release, sperm cryopreservation (biobanking), and in vitro fertilization provide a low‐risk alternative to harvesting whole animals (Clulow et al., 2022). Protocols for L. raniformis sperm collection and cryopreservation exist (J. Clulow, pers.…”
Harvesting wild populations is increasingly used to support conservation initiatives, including translocations, captive assurance colonies, and breeding programs. Best‐practice guidelines recommend that population viability analyses should be developed to assess the potential impact of harvest on source populations, allowing quantification of the risk incurred by the conservation programme. We developed a stochastic population model to assess the relative impact of harvesting southern bell frogs (Litoria raniformis) from three well‐studied populations. We compared the probability of local extinction when harvesting from three life stages (spawn, tadpoles, and adults) and at 21 harvest proportions (from 0 to 1, in 0.05 increments). Source populations with an estimated average of 100 adult frogs and with three or fewer breeding opportunities every 5 years showed increased risk of local extinction and lower minimum adult populations from all harvest strategies. Sources with an estimated average population >600 adult frogs and breeding opportunities in at least eight out of every 10 years were more resilient to harvest. For these populations, harvesting up to 25% of spawning masses or late‐stage tadpoles had a negligible impact on the probability of local extinction and caused a slight decrease in the minimum adult population. Harvesting adults impacted source populations more strongly than harvesting spawn or tadpoles. Our model highlights the importance of frequent breeding opportunities to offset the effects of harvesting L. raniformis. Populations sustained by environmental water delivery should be prioritized for the two consecutive breeding seasons following harvest in the absence of natural wetland inundation. We demonstrate a tractable approach to assess and compare the relative risk of wild harvest for threatened amphibians, with implications for the conservation of our focal species, L. raniformis. We encourage conservation practitioners to implement population viability analyses prior to wild harvest, whenever sufficient demographic information is available to build the requisite models.
“…Improved river management, such as managed flow delivery in regulated systems, has attempted to improve wetland habitats and the condition of rivers (Espinoza et al, 2022; Francis et al, 2022). More broadly, technological advances such as biobanking gametes, controlling diseases, and advances in genetic and bioinformatic tools should assist future conservation measures (Clulow et al, 2022). However, knowledge of the most effective conservation actions, the effectiveness of attempts to aid population recovery, and whether these actions are required at all, remains lacking for many species.…”
Section: Priorities and Challenges For The Conservation Of Australian...mentioning
Australia's freshwater turtles have high endemicity and many are threatened by extinction. Following a symposium held at the 2022 conference of the Australian Society of Herpetologists, we summarized the current status of research and conservation for Australian freshwater turtles and identified opportunities for future research. Eight species (32%) of Australia's 25 native freshwater turtles are listed as threatened by Australia's Federal Government. Symposium discussions on the primary gaps in research identified the lack of baseline data to inform population modelling as a key deficiency. Knowledge of the most effective conservation actions, the effectiveness of attempts to aid population recovery, and whether these actions are required at all, remains lacking for many species. A heavy bias exists between some well‐studied species compared with others for which little or no information is published. Community science, engagement with First Nations people, advances in technology, and recognition of the importance of turtles are contributing to better knowledge.
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