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Do estimates of contemporary effective population size tell us what we want to know?
Estimation of effective population size (N (e)) from genetic marker data is a major focus for biodiversity conservation because it is essential to know at what rates inbreeding is increasing and additive genetic variation is lost. But are these the rates assessed when applying commonly used N (e) es...
Autores principales: | , , |
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Formato: | Online Artículo Texto |
Lenguaje: | English |
Publicado: |
John Wiley and Sons Inc.
2019
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Materias: | |
Acceso en línea: | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6850010/ https://www.ncbi.nlm.nih.gov/pubmed/30663828 http://dx.doi.org/10.1111/mec.15027 |
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author | Ryman, Nils Laikre, Linda Hössjer, Ola |
author_facet | Ryman, Nils Laikre, Linda Hössjer, Ola |
author_sort | Ryman, Nils |
collection | PubMed |
description | Estimation of effective population size (N (e)) from genetic marker data is a major focus for biodiversity conservation because it is essential to know at what rates inbreeding is increasing and additive genetic variation is lost. But are these the rates assessed when applying commonly used N (e) estimation techniques? Here we use recently developed analytical tools and demonstrate that in the case of substructured populations the answer is no. This is because the following: Genetic change can be quantified in several ways reflecting different types of N (e) such as inbreeding (N (eI)), variance (N (eV)), additive genetic variance (N (eAV)), linkage disequilibrium equilibrium (N (eLD)), eigenvalue (N (eE)) and coalescence (N (eCo)) effective size. They are all the same for an isolated population of constant size, but the realized values of these effective sizes can differ dramatically in populations under migration. Commonly applied N (e)‐estimators target N (eV) or N (eLD )of individual subpopulations. While such estimates are safe proxies for the rates of inbreeding and loss of additive genetic variation under isolation, we show that they are poor indicators of these rates in populations affected by migration. In fact, both the local and global inbreeding (N (eI)) and additive genetic variance (N (eAV)) effective sizes are consistently underestimated in a subdivided population. This is serious because these are the effective sizes that are relevant to the widely accepted 50/500 rule for short and long term genetic conservation. The bias can be infinitely large and is due to inappropriate parameters being estimated when applying theory for isolated populations to subdivided ones. |
format | Online Article Text |
id | pubmed-6850010 |
institution | National Center for Biotechnology Information |
language | English |
publishDate | 2019 |
publisher | John Wiley and Sons Inc. |
record_format | MEDLINE/PubMed |
spelling | pubmed-68500102019-11-15 Do estimates of contemporary effective population size tell us what we want to know? Ryman, Nils Laikre, Linda Hössjer, Ola Mol Ecol ORIGINAL ARTICLES Estimation of effective population size (N (e)) from genetic marker data is a major focus for biodiversity conservation because it is essential to know at what rates inbreeding is increasing and additive genetic variation is lost. But are these the rates assessed when applying commonly used N (e) estimation techniques? Here we use recently developed analytical tools and demonstrate that in the case of substructured populations the answer is no. This is because the following: Genetic change can be quantified in several ways reflecting different types of N (e) such as inbreeding (N (eI)), variance (N (eV)), additive genetic variance (N (eAV)), linkage disequilibrium equilibrium (N (eLD)), eigenvalue (N (eE)) and coalescence (N (eCo)) effective size. They are all the same for an isolated population of constant size, but the realized values of these effective sizes can differ dramatically in populations under migration. Commonly applied N (e)‐estimators target N (eV) or N (eLD )of individual subpopulations. While such estimates are safe proxies for the rates of inbreeding and loss of additive genetic variation under isolation, we show that they are poor indicators of these rates in populations affected by migration. In fact, both the local and global inbreeding (N (eI)) and additive genetic variance (N (eAV)) effective sizes are consistently underestimated in a subdivided population. This is serious because these are the effective sizes that are relevant to the widely accepted 50/500 rule for short and long term genetic conservation. The bias can be infinitely large and is due to inappropriate parameters being estimated when applying theory for isolated populations to subdivided ones. John Wiley and Sons Inc. 2019-04-26 2019-04 /pmc/articles/PMC6850010/ /pubmed/30663828 http://dx.doi.org/10.1111/mec.15027 Text en © 2019 The Authors. Molecular Ecology Published by John Wiley & Sons Ltd This is an open access article under the terms of the http://creativecommons.org/licenses/by-nc-nd/4.0/ License, which permits use and distribution in any medium, provided the original work is properly cited, the use is non‐commercial and no modifications or adaptations are made. |
spellingShingle | ORIGINAL ARTICLES Ryman, Nils Laikre, Linda Hössjer, Ola Do estimates of contemporary effective population size tell us what we want to know? |
title | Do estimates of contemporary effective population size tell us what we want to know? |
title_full | Do estimates of contemporary effective population size tell us what we want to know? |
title_fullStr | Do estimates of contemporary effective population size tell us what we want to know? |
title_full_unstemmed | Do estimates of contemporary effective population size tell us what we want to know? |
title_short | Do estimates of contemporary effective population size tell us what we want to know? |
title_sort | do estimates of contemporary effective population size tell us what we want to know? |
topic | ORIGINAL ARTICLES |
url | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6850010/ https://www.ncbi.nlm.nih.gov/pubmed/30663828 http://dx.doi.org/10.1111/mec.15027 |
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