Abstract

In this contribution, we determine the genetic population structure in the Skunk Clownfish (Amphiprion akallopsisos) across the Indian Ocean, and on a smaller geographic scale in the Western Indian Ocean (WIO). Highly restricted gene flow was discovered between populations on either side of the Indian Ocean using the control region as a mitochondrial marker (mtDNA). We verify this conclusion using 13 microsatellite markers and infer fine scale genetic structuring within the WIO. In total 387 samples from 21 sites were analysed using mtDNA and 13 microsatellite loci. Analysis included estimation of genetic diversity and population differentiation. A haplotype network was inferred using mtDNA. Nuclear markers were used in Bayesian clustering and a principal component analysis. Both markers confirmed strong genetic differentiation between WIO and Eastern Indian Ocean (EIO) populations, and a shallower population structure among Malagasy and East African mainland populations. Limited gene flow across the Mozambique Channel may be explained by its complex oceanography, which could cause local retention of larvae, limiting dispersal between Madagascar and the East African coast. Two other potential current-mediated barriers to larval dispersal suggested in the WIO, the split of the SEC at approximately 10° S and the convergence of the Somali Current with the East African Coast Current at approximately 3° S, were not found to form a barrier to gene flow in this species.

Highlights

  • Coral reefs are threatened worldwide by several human induced factors, such as overfishing, tourism, or pollution

  • We aim to investigate whether: (1) the genetic break between Western Indian Ocean (WIO) and Eastern Indian Ocean (EIO) is detected using microsatellite markers; (2) barriers to gene flow could be detected within the WIO using this extended dataset and a combination of different markers

  • Deviation from HardyWeinberg equilibrium in both the WIO and the EIO was detected in this enlarged dataset, confirming the results obtained in Huyghe & Kochzius (2016) (Fu’s F & Tajima’s D)

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Summary

Introduction

Coral reefs are threatened worldwide by several human induced factors, such as overfishing, tourism, or pollution. They are at risk to convert to an alternative, macroalgae-dominated state that would alter their ecosystem characteristics. This process is further accelerated by human-induced environmental stresses, such as global warming and ocean acidification, making urgent conservation measures a necessity [1]. A very efficient and much used conservation instrument is the establishment of marine protected areas (MPAs), protecting certain coral reef zones from fishing pressure and other potentially harmful activities. Established and managed MPAs serve several purposes: they fulfil a role as sanctuaries for both species and genetic diversity, but are intended to strengthen ecosystem resilience and promote

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