12 results on '"Bravington M"'
Search Results
2. Fast Likelihood-Based Inference for Latent Count Models Using the Saddlepoint Approximation
- Author
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Zhang, W., primary, Bravington, M. V., additional, and Fewster, R. M., additional
- Published
- 2019
- Full Text
- View/download PDF
3. Genetic relatedness reveals total population size of white sharks in eastern Australia and New Zealand
- Author
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Hillary, R. M., primary, Bravington, M. V., additional, Patterson, T. A., additional, Grewe, P., additional, Bradford, R., additional, Feutry, P., additional, Gunasekera, R., additional, Peddemors, V., additional, Werry, J., additional, Francis, M. P., additional, Duffy, C. A. J., additional, and Bruce, B. D., additional
- Published
- 2018
- Full Text
- View/download PDF
4. Molecular biomarkers for chronological age in animal ecology
- Author
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Jarman, Simon, Polanowski, A., Faux, C., Robbins, J., De Paoli-Iseppi, R., Bravington, M., Deagle, B., Jarman, Simon, Polanowski, A., Faux, C., Robbins, J., De Paoli-Iseppi, R., Bravington, M., and Deagle, B.
- Abstract
© 2015 John Wiley & Sons Ltd. The chronological age of an individual animal predicts many of its biological characteristics, and these in turn influence population-level ecological processes. Animal age information can therefore be valuable in ecological research, but many species have no external features that allow age to be reliably determined. Molecular age biomarkers provide a potential solution to this problem. Research in this area of molecular ecology has so far focused on a limited range of age biomarkers. The most commonly tested molecular age biomarker is change in average telomere length, which predicts age well in a small number of species and tissues, but performs poorly in many other situations. Epigenetic regulation of gene expression has recently been shown to cause age-related modifications to DNA and to cause changes in abundance of several RNA types throughout animal lifespans. Age biomarkers based on these epigenetic changes, and other new DNA-based assays, have already been applied to model organisms, humans and a limited number of wild animals. There is clear potential to apply these marker types more widely in ecological studies. For many species, these new approaches will produce age estimates where this was previously impractical. They will also enable age information to be gathered in cross-sectional studies and expand the range of demographic characteristics that can be quantified with molecular methods. We describe the range of molecular age biomarkers that have been investigated to date and suggest approaches for developing the newer marker types as age assays in nonmodel animal species.
- Published
- 2015
5. A Model-Based Approach to Designing a Fishery-Independent Survey
- Author
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Peel, D., primary, Bravington, M. V., additional, Kelly, N., additional, Wood, S. N., additional, and Knuckey, I., additional
- Published
- 2012
- Full Text
- View/download PDF
6. Microsatellite DNA markers: evaluating their potential for estimating the proportion of hatchery‐reared offspring in a stock enhancement programme
- Author
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Bravington, M. V., primary and Ward, R. D., additional
- Published
- 2004
- Full Text
- View/download PDF
7. Plenary report
- Author
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Hammond, P., Leaper, R., Lusseau, D., Parsons, C., Simmonds, M., Brownell, R., Palka, D., Baker, S., Bickham, J., Breiwick, J., Clapham, P., Ferguson, M., Fleming, A., George, C., Givens, G., Lang, A., Matilla, D., Moore, S., Perrin, W., Robbins, J., Rosa, C., Rosenbaum, H., Rowles, T., Scordino, J., Suydam, R., Taylor, J., Wade, P., Waples, R., Weller, D., Ylitalo, G., Amaral, A., Baldwin, R., Bami, I., Bannister, J., Barendse, J., Bejder, L., Best, P., Brandão, A., Brandon, J., Bravington, M., Burt, L., Brito, C., Butterworth, D., Campbell, J., Cañadas, A., Carlson, C., Carvalho, I., Cerchio, S., Cipriano, F., Collins, T., Darling, J., Quirós, Y. B., Carryn de Moor, Ensor, P., Frasier, T., Funahashi, N., Gaggiotti, O., Groch, K., Hedley, S., Hoelzel, R., Holloway, S., Ivashchenko, Y., Jackson, J., Kasuya, T., Kaufman, G., Koski, B., Lehodey, P., Lockyer, C., Mate, B., Muller, A., Ofori-Danson, P., Punt, A., Reeves, R., Rose, N., Sekiguchi, K., Sironi, M., Solarin, B., Tchibozo, S., Urbán-Ramirez, J., Weinrich, M., Werner, S., Wiig, Ø., Williams, R., Wright, A., Young, J., Strbenac, A., Kock, K. -H, Cooke, J., Larsen, F., Acquarone, M., Kato, H., Allison, C., Brockington, S., Donovan, G., Grandy, N., Hughes, M., Jones, J., Tamura, T., and Goto, M.
8. Low levels of sibship encourage use of larvae in western Atlantic bluefin tuna abundance estimation by close-kin mark-recapture.
- Author
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McDowell JR, Bravington M, Grewe PM, Lauretta M, Walter JF 3rd, Baylis SM, Gosselin T, Malca E, Gerard T, Shiroza A, Lamkin JT, Biesack EE, Zapfe G, Ingram W, Davies C, and Porch C
- Subjects
- Animals, Larva, Gulf of Mexico, Atlantic Ocean, Tuna genetics
- Abstract
Globally, tunas are among the most valuable fish stocks, but are also inherently difficult to monitor and assess. Samples of larvae of Western Atlantic bluefin tuna Thunnus thynnus (Linnaeus, 1758) from standardized annual surveys in the northern Gulf of Mexico provide a potential source of "offspring" for close-kin mark-recapture (CKMR) estimates of abundance. However, the spatial patchiness and highly skewed numbers of larvae per tow suggest sampled larvae may come from a small number of parents, compromising the precision of CKMR. We used high throughput genomic profiling to study sibship within and among larval tows from the 2016 standardized Gulf-wide survey compared to targeted sampling carried out in 2017. Full- and half-siblings were found within both years, with 12% of 156 samples in 2016 and 56% of 317 samples in 2017 having at least one sibling. There were also two pairs of cross cohort half-siblings. Targeted sampling increased the number of larvae collected per sampling event but resulted in a higher proportion of siblings. The combined effective sample size across both years was about 75% of the nominal size, indicating that Gulf of Mexico larval collections could be a suitable source of juveniles for CKMR in Western Atlantic bluefin tuna., (© 2022. The Author(s).)
- Published
- 2022
- Full Text
- View/download PDF
9. Inferring contemporary and historical genetic connectivity from juveniles.
- Author
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Feutry P, Berry O, Kyne PM, Pillans RD, Hillary RM, Grewe PM, Marthick JR, Johnson G, Gunasekera RM, Bax NJ, and Bravington M
- Subjects
- Animal Distribution, Animals, Australia, Conservation of Natural Resources, Female, Gene Flow, Genome, Mitochondrial, Male, Papua New Guinea, Polymorphism, Single Nucleotide, Endangered Species, Genetics, Population, Sharks genetics
- Abstract
Measuring population connectivity is a critical task in conservation biology. While genetic markers can provide reliable long-term historical estimates of population connectivity, scientists are still limited in their ability to determine contemporary patterns of gene flow, the most practical time frame for management. Here, we tackled this issue by developing a new approach that only requires juvenile sampling at a single time period. To demonstrate the usefulness of our method, we used the Speartooth shark (Glyphis glyphis), a critically endangered species of river shark found only in tropical northern Australia and southern Papua New Guinea. Contemporary adult and juvenile shark movements, estimated with the spatial distribution of kin pairs across and within three river systems, was contrasted with historical long-term connectivity patterns, estimated from mitogenomes and genome-wide SNP data. We found strong support for river fidelity in juveniles with the within-cohort relationship analysis. Male breeding movements were highlighted with the cross-cohort relationship analysis, and female reproductive philopatry to the river systems was revealed by the mitogenomic analysis. We show that accounting for juvenile river fidelity and female philopatry is important in population structure analysis and that targeted sampling in nurseries and juvenile aggregations should be included in the genomic toolbox of threatened species management., (© 2016 John Wiley & Sons Ltd.)
- Published
- 2017
- Full Text
- View/download PDF
10. Molecular biomarkers for chronological age in animal ecology.
- Author
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Jarman SN, Polanowski AM, Faux CE, Robbins J, De Paoli-Iseppi R, Bravington M, and Deagle BE
- Subjects
- Animals, Ecology methods, Humans, Telomere ultrastructure, Aging genetics, Biomarkers, Epigenesis, Genetic
- Abstract
The chronological age of an individual animal predicts many of its biological characteristics, and these in turn influence population-level ecological processes. Animal age information can therefore be valuable in ecological research, but many species have no external features that allow age to be reliably determined. Molecular age biomarkers provide a potential solution to this problem. Research in this area of molecular ecology has so far focused on a limited range of age biomarkers. The most commonly tested molecular age biomarker is change in average telomere length, which predicts age well in a small number of species and tissues, but performs poorly in many other situations. Epigenetic regulation of gene expression has recently been shown to cause age-related modifications to DNA and to cause changes in abundance of several RNA types throughout animal lifespans. Age biomarkers based on these epigenetic changes, and other new DNA-based assays, have already been applied to model organisms, humans and a limited number of wild animals. There is clear potential to apply these marker types more widely in ecological studies. For many species, these new approaches will produce age estimates where this was previously impractical. They will also enable age information to be gathered in cross-sectional studies and expand the range of demographic characteristics that can be quantified with molecular methods. We describe the range of molecular age biomarkers that have been investigated to date and suggest approaches for developing the newer marker types as age assays in nonmodel animal species., (© 2015 John Wiley & Sons Ltd.)
- Published
- 2015
- Full Text
- View/download PDF
11. Designing an effective mark-recapture study of Antarctic blue whales.
- Author
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Peel D, Bravington M, Kelly N, and Double MC
- Subjects
- Animal Distribution, Animals, Antarctic Regions, Conservation of Natural Resources, Endangered Species, Female, Male, Models, Biological, Population Dynamics, Animal Identification Systems veterinary, Whales physiology
- Abstract
To properly conserve and manage wild populations, it is important to have information on abundance and population dynamics. In the case of rare and cryptic species, especially in remote locations, surveys can be difficult and expensive, and run the risk of not producing sample sizes large enough to produce precise estimates. Therefore, it is crucial to conduct preliminary analysis to determine if the study will produce useable estimates. The focus of this paper is a proposed mark-recapture study of Antarctic blue whales (Balaenoptera musculus intermedia). Antarctic blue whales were hunted to near extinction up until the mid- 1960s, when commercial exploitation of this species ended. Current abundance estimates are a decade old. Furthermore, at present, there are no formal circumpolar-level cetacean surveys operating in Antarctic waters and, specifically, there is no strategy to monitor the potential recovery of Antarctic blue whales. Hence the work in this paper was motivated by the need to inform decisions on strategies for future monitoring of Antarctic blue whale population. The paper describes a model to predict the precision and bias of estimates from a proposed survey program. The analysis showed that mark-recapture is indeed a suitable method to provide a circumpolar abundance estimate of Antarctic blue whales, with precision of the abundance, at the midpoint of the program, predicted to be between 0.2 and 0.3. However, this was only if passive acoustic tracking was utilized to increase the encounter rate. The analysis also provided guidance on general design for an Antarctic blue whale program, showing that it requires a 12-year duration; although surveys do not necessarily need to be run every year if multiple vessels are available to clump effort. Mark-recapture is based on a number of assumptions; it was evident from the analysis that ongoing analysis and monitoring of the data would be required to check such assumptions hold (e.g., test for heterogeneity), with the modeling adjusted as needed.
- Published
- 2015
- Full Text
- View/download PDF
12. Accounting for location error in Kalman filters: integrating animal borne sensor data into assimilation schemes.
- Author
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Sengupta A, Foster SD, Patterson TA, and Bravington M
- Subjects
- Algorithms, Animals, Computer Simulation, Satellite Communications, Fishes, Oceanography methods, Oceans and Seas
- Abstract
Data assimilation is a crucial aspect of modern oceanography. It allows the future forecasting and backward smoothing of ocean state from the noisy observations. Statistical methods are employed to perform these tasks and are often based on or related to the Kalman filter. Typically Kalman filters assumes that the locations associated with observations are known with certainty. This is reasonable for typical oceanographic measurement methods. Recently, however an alternative and abundant source of data comes from the deployment of ocean sensors on marine animals. This source of data has some attractive properties: unlike traditional oceanographic collection platforms, it is relatively cheap to collect, plentiful, has multiple scientific uses and users, and samples areas of the ocean that are often difficult of costly to sample. However, inherent uncertainty in the location of the observations is a barrier to full utilisation of animal-borne sensor data in data-assimilation schemes. In this article we examine this issue and suggest a simple approximation to explicitly incorporate the location uncertainty, while staying in the scope of Kalman-filter-like methods. The approximation stems from a Taylor-series approximation to elements of the updating equation.
- Published
- 2012
- Full Text
- View/download PDF
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