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Population Genetic Parameters (population + genetic_parameter)
Selected AbstractsGenetic structure of two populations of the Namibian giraffe, Giraffa camelopardalis angolensisAFRICAN JOURNAL OF ECOLOGY, Issue 4 2009Rick A. Brenneman Abstract Two geographically distinct populations of giraffe (Giraffa camelopardalis) were sampled for this study, the northern Namib Desert and Etosha National Park. Population genetic parameters and relationships within subpopulations were estimated to better understand the genetic architecture of this isolated subspecies. Gene flow between the geographically separated populations can be attributed to recent translocation of giraffe between the two populations. Inbreeding estimates in the six subpopulations studied were low though we found evidence that genetic drift may be affecting the genetic diversity of the isolated populations in northern Namibia. Population dynamics of the sampling locations was inferred with relationship coefficient analyses. Recent molecular systematics of the Namibian giraffe populations indicates that they are distinct from the subspecies Giraffa camelopardalis giraffa and classified as G. c. angolensis. Based on genetic analyses, these giraffe populations of northern Namibia, the desert-dwelling giraffe and those protected in Etosha National Park, are a distinct subspecies from that previously assumed; thus we add data on G. c. angolensis to our scientific knowledge of this giraffe of southern Africa. Résumé Deux populations de girafes (Giraffa camelopardalis) distinctes sur le plan géographique ont servi d'échantillons pour cette étude, celle du nord du Désert du Namib et celle du Parc National d'Etosha. Nous avons estimé les paramètres génétiques des populations et les relations au sein des sous-populations pour mieux comprendre l'architecture génétique de cette sous-espèce isolée. Les flux génétiques entre les populations séparées géographiquement peuvent être attribués à la récente translocation de girafes entre ces deux populations. L'inbreeding estimé dans les six sous-populations étudiées était faible, encore que nous ayons découvert des preuves que la dérive génétique pourrait bien affecter la diversité génétique des populations isolées dans le nord de la Namibie. La dynamique des populations des endroits où furent faits les échantillonnages fut déduite en fonction de l'analyse des coefficients. La nouvelle systématique moléculaire des populations de girafes de Namibie indique qu'elles sont distinctes de la sous-espèce Giraffa camelopardalis giraffa et classées comme G.c. angolensis. Selon les analyses génétiques, ces populations de girafes du nord de la Namibie, les girafes qui vivent dans le désert et celles qui sont protégées dans le Parc National d'Etosha sont une sous-espèce distincte de celle que l'on croyait auparavant, et nous ajoutons ainsi des données sur G.c. angolensisà la connaissance scientifique de cette girafe d'Afrique australe. [source] WHY DOES A METHOD THAT FAILS CONTINUE TO BE USED?EVOLUTION, Issue 11 2008L. Lacey Knowles As a critical framework for addressing a diversity of evolutionary and ecological questions, any method that provides accurate and detailed phylogeographic inference would be embraced. What is difficult to understand is the continued use of a method that not only fails, but also has never been shown to work,nested clade analysis is applied widely even though the conditions under which the method will provide reliable results have not yet been demonstrated. This contradiction between performance and popularity is even more perplexing given the recent methodological and computational advances for making historical inferences, which include estimating population genetic parameters and testing different biogeographic scenarios. Here I briefly review the history of criticisms and rebuttals that focus specifically on the high rate of incorrect phylogeographic inference of nested-clade analysis, with the goal of understanding what drives its unfettered popularity. In this case, the appeal of what nested-clade analysis claims to do,not what the method actually achieves,appears to explain its paradoxical status as a favorite method that fails. What a method promises, as opposed to how it performs, must be considered separately when evaluating whether the method represents a valuable tool for historical inference. [source] Genetic structure and gene flow in wild beet populations: the potential influence of habitat on transgene spread and risk assessmentJOURNAL OF APPLIED ECOLOGY, Issue 6 2006A. N. CURETON Summary 1The consequences of the movement of transgenes from genetically modified (GM) crops into wild populations of plants continues to be of concern to ecologists and conservationists because of the possible threat posed to those populations in terms of their continued survival and because of the further knock-on effects that might occur to habitats in which they occur. 2We examined five UK sea beet Beta vulgaris ssp. maritima populations from each of two major habitat types, cliff top and drift line. We assessed population genetic parameters, genetic diversity, gene flow, population differentiation and isolation by distance, to enable determination of the likelihood and consequences of spread to wild populations of genes from cultivated sugar beet group Beta vulgaris ssp. vulgaris, which could in the future be transgenic. 3Drift line populations were more diverse than cliff top populations and also showed greater levels of gene flow. 4Isolation by distance was identified in both habitats, but the relationship between genetic and geographical distance was detectable over longer distances for drift line populations. However, clear indications of vicariance (the subdivision of a population into distinct taxa by the appearance of a geological barrier) between cliff and drift line populations were also evident, because of the restriction of gene flow between the two habitats occurring more in one direction than the other. 5Synthesis and applications. The likelihood of transgene spread from crop to wild populations is habitat dependent and conservation management decisions could therefore vary from one population to another, for example water courses were found to facilitate seed dispersal. This should be taken into account when estimating isolation distances for GM beet, and when predicting transgene frequencies (exposure estimates) for environmental risk assessments of GM beet. [source] Development and characterization of microsatellite loci in endangered Astrophytum asterias (Cactaceae)MOLECULAR ECOLOGY RESOURCES, Issue 3 2006MARTIN TERRY Abstract We report the development of polymorphic microsatellite markers for the endangered North American cactus Astrophytum asterias (Cactaceae). Six loci, averaging 8.5 alleles per locus, were found to amplify genomic DNA consistently in 94 individuals from four geographically defined demes in South Texas. These markers will permit the generation of appropriate data for estimating population genetic parameters, population structure and the degree of inbreeding in the small, fragmented populations of A. asterias that currently exist. These are the first microsatellites reported for the genus Astrophytum and for the tribe Cacteae. [source] Spatial aggregation in Fusarium pseudograminearum populations from the Australian grain beltPLANT PATHOLOGY, Issue 1 2009A. R. Bentley Previous studies have evaluated the overall structure of populations of Fusarium pseudograminearum (teleomorph, Gibberella coronicola), causal agent of cereal crown rot, but there is no information available on spatial relationships of genetic variation in field populations. Three 1-m-row sections in crown-rot-affected wheat fields in the Australian grain belt were intensively sampled to estimate population genetic parameters and the spatial aggregation, or clustering, of disease aggregates and genotypes. Estimates of population genetic parameters based on amplified fragment length polymorphisms (AFLPs) indicated that the genetic diversity in isolates from the 1-m-row populations described a significant portion of the diversity recorded for corresponding field and regional populations. In point pattern analysis, there was physical clustering and aggregation of F. pseudograminearum isolates from two of the three sites. Analysis of the spatial distribution of clonal haplotypes (DICE similarity , 97%) indicated significant aggregation of clones in all three 1-m-row populations. Based on matrix comparison tests, both mating types and genetic distances had significant spatial aggregation for at least two of the three 1-m-row populations. This is consistent with the presence of non-random spatial genetic structure due to clonal aggregation. High levels of genetic diversity and spatial structuring of disease and genotypes in at least two of the three 1-m-row populations is consistent with the hypothesis that stubble is a primary inoculum source in no-tillage farming systems, resulting in aggregated patterns of disease and allowing for haplotypes to be maintained in the field over a number of annual cropping cycles. [source] Genetic variability revealed with microsatellite markers in an introduced population of the abalone Haliotis discus hannai InoAQUACULTURE RESEARCH, Issue 3 2009S Marchant Abstract One of the challenges for the culture of any species is to control the loss of genetic variability, which may result in a decrease in the quality of commercially important traits. The goal of this study is to assess the genetic diversity of a hatchery population of the Pacific abalone (Haliotis discus hannai) from the Center for Abalone Production of the Universidad Católica del Norte (CAP-UCN) that is maintained under a breeding programme. We used six polymorphic microsatellite markers within the cultivated population. The loci Awb033 and Awb079 had the highest number of alleles (11 and 10 respectively) and the loci Awb022 and Awb026 the lowest (two and four respectively). The mean number of alleles per locus was 6.83. The average observed and expected heterozygosities were 0.71 and 0.70, respectively, and the average FIS (f) index was ,0.023. We compared the population genetic parameters of the CAP-UCN population with previously published data of wild and hatchery populations of the same species. Results indicate lower genetic diversity estimated as allelic richness in the introduced population with a loss of 11,58% alleles per locus. Despite the high allelic loss, the estimated inbreeding coefficient suggests that the breeding programme carried out in the CAP-UCN has controlled and maintained heterozygosity levels successfully. A temporal study is necessary to determine whether the genetic diversity loss detected was caused during the initial introduction of breeders or to the breeding programme actually implemented. [source] | ||||||||||