Linda Penfold

Dr. Linda Penfold

South-East Zoo Alliance for Reproduction and Conservation, Yulee, FL 32097, USA

Research Focus & Metrics

Academic Career Length

15Years (2012-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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28 December 2013 in Zoo Biology
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Journal Article
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LPLinda Penfold
Linda Penfold
DPDavid Powell
David Powell
KTKathy Traylor‐Holzer
Kathy Traylor‐Holzer
CACheryl S. Asa
Cheryl S. Asa

15 February 2024 in Annual Review of Animal Biosciences
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Journal Article
Open access
VCVeronica Cowl
Veronica Cowl
PCPierre Comizzoli
Pierre Comizzoli
RARuth Appeltant
Ruth Appeltant
RBRhiannon L. Bolton
Rhiannon L. Bolton
Robert K. BrowneRobert K. Browne
Robert K. Browne
SWSuzannah A. Williams
Suzannah A. Williams
Cloning as it relates to the animal kingdom generally refers to the production of genetically identical individuals. Because cloning is increasingly the subject of renewed attention as a tool for rescuing endangered or extinct species, it seems timely to dissect the role of the numerous reproductive techniques encompassed by this term in animal species conservation. Although cloning is typically associated with somatic cell nuclear transfer, the recent advent of additional techniques that allow genome replication without genetic recombination demands that the use of induced pluripotent stem cells to generate gametes or embryos, as well as older methods such as embryo splitting, all be included in this discussion. Additionally, the phenomenon of natural cloning (e.g., a subset of fish, birds, invertebrates, and reptilian species that reproduce via parthenogenesis) must also be pointed out. Beyond the biology of these techniques are practical considerations and the ethics of using cloning and associated procedures in endangered or extinct species. All of these must be examined in concert to determine whether cloning has a place in species conservation. Therefore, we synthesize progress in cloning and associated techniques and dissect the practical and ethical aspects of these methods as they pertain to endangered species conservation.

31 August 2019
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Book Chapter
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LPLinda Penfold
Linda Penfold
JWJennifer T. Wyffels
Jennifer T. Wyffels

1 January 2016 in General and Comparative Endocrinology
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Journal Article
Closed access
SBSerena A. Barnes
Serena A. Barnes
JTJ. Andrew Teare
J. Andrew Teare
SSSheryl Staaden
Sheryl Staaden
LMLara Metrione
Lara Metrione
LPLinda Penfold
Linda Penfold

19 July 2012 in Zoo Biology
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Journal Article
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LPLinda Penfold
Linda Penfold
SHSara Hallager
Sara Hallager
JBJeanette Boylan
Jeanette Boylan
MWMartine de Wit
Martine de Wit
LMLara Metrione
Lara Metrione
MOMarcie Oliva
Marcie Oliva

7 April 2022 in Journal of Mammalogy
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Journal Article
Open access
PDF file
LPLinda Penfold
Linda Penfold
MCMarc Criffield
Marc Criffield
MCMark W Cunningham
Mark W Cunningham
DJDeborah Jansen
Deborah Jansen
MLMark Lotz
Mark Lotz
DODave Onorato
Dave Onorato
In 1995, eight female pumas from Texas (Puma concolor stanleyana) were introduced into five areas in South Florida to remediate morphological and biomedical correlates of inbreeding depression that threatened the long-term survival of Florida panthers (P. c. coryi). Initial analysis of the results of this genetic introgression initiative has highlighted its success, including growth of the population, increased genetic heterozygosity, and reduced frequencies of physical traits associated with inbreeding, including cryptorchidism. However, panthers remain isolated from other puma populations and natural gene flow is not currently plausible. Using data collected from 65 panthers in the post-genetic introgression era (1998–2020), we assessed the benefits accrued to male panther reproductive parameters via this management initiative, the effect of genetic variables, and compared results to historic data. Microsatellite data were used to determine individual heterozygosity levels and qualify panther genetic ancestry as admixed (i.e., panthers descended from crosses with female Texas puma) or canonical (i.e., panthers that comprised most of the population prior to genetic introgression). A total of 47 admixed and 10 canonical panthers were identified; mean individual heterozygosity of canonical panthers (0.39) was significantly different from admixed panthers (0.63; t54 = 4.7, P-value < 0.001). Admixed panthers exhibited higher mean values for total testicular volume, structurally normal spermatozoa, and total sperm in comparison to canonical panthers. The progressive improvement of sperm metrics demonstrates that the benefits of genetic introgression continue to have a positive impact on the population >25 years since the release of the Texas pumas. However, the Florida panther population remains small, isolated, and vulnerable to deterministic and stochastic events that warrants continued monitoring to assess when additional genetic introgression initiatives will need to be implemented in the future.