Abstract

Manta rays (Mobula spp.) are highly valued in nature-based tourism globally. In Indonesia, although manta rays are protected, critical information is lacking on their habitat use, population dynamics and movements. We investigate the population structure and residency patterns of reef manta rays (Mobula alfredi) in the Nusa Penida Marine Protected Area (MPA). From photo-identification data logged by citizen scientists and trained observers (mantamatcher.org), we identified 624 reef manta rays from 5,913 sightings (January 2012–April 2018) based on their unique ventral coloration patterns. Year-round records were collected from two shallow (<20 m) reefs – Manta Bay (MB; n = 3,029 sightings) and Manta Point (MP; n = 3,058) – that are used frequently by tourism operators. Maximum likelihood techniques and a Markov movement analysis were used to model residency patterns and movement between these sites within the MPA. Manta rays at MB were predominantly male (64%, n = 261 individuals), with immature males (14%, n = 59) being sighted most frequently (39%, n = 1,170). In contrast, few immature individuals were sighted at MP (6%, n = 28), and they were sighted on few occasions (2%, n = 45), while mature female manta rays comprised 26% (n = 127) of the MP community and were the most frequently sighted (48%, n = 1,413). Lagged identification rates indicated high site fidelity at each location. However, 44% (n = 278) of individuals moved between the two sites and cumulative discovery curves showed a continued recruitment of individuals over the 6 years of the study. In addition, the behaviors displayed by the manta rays differed markedly between the two sites: MB appears to be a foraging ground, especially for juveniles, and potentially a nursery, while MP is used mainly for cleaning and courtship, indicating a social and reproductive site. Reproductive behavior coincided with the peak annual sightings in May. To prevent disturbance to this threatened species by tourism, regulations for the number of boats and interactions, especially during key reproductive times should be considered. Further, strict fishing regulation in the area is recommended as fishing gear entanglement was identified as a threat to this population.

Highlights

  • Many marine megafauna species, such as sea turtles (Bowen and Karl, 2007), cetaceans (Baird et al, 2008), large teleost fish (Robichaud and Rose, 2001; Rooker et al, 2008), and elasmobranchs (Hueter et al, 2005), range widely, but within these large areas show high fidelity to defined areas for reproduction and feeding (Chapman et al, 2015)

  • Data from 6,087 sightings of manta rays were collected within the Nusa Penida Marine Protected Areas (MPAs) from 25 June 2004 to 9 April 2018

  • The number of annual manta ray sightings varied across the study period (Figure 2A and Supplementary Table 1), with sightings being positively correlated with survey effort (r = 0.92, p < 0.01) for all study years

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Summary

Introduction

Many marine megafauna species, such as sea turtles (Bowen and Karl, 2007), cetaceans (Baird et al, 2008), large teleost fish (Robichaud and Rose, 2001; Rooker et al, 2008), and elasmobranchs (Hueter et al, 2005), range widely, but within these large areas show high fidelity to defined areas for reproduction and feeding (Chapman et al, 2015). Pelagic, filter-feeding mobulid rays (Mobula spp.) found in equatorial and tropical waters (e.g., Couturier et al, 2012), that are threatened with extinction. Owing in part to these conservative life history traits and to overfishing across their range (Dulvy et al, 2014), both Mobula alfredi (Krefft, 1868) and the larger M. birostris (Walbaum, 1792) are currently listed as vulnerable to extinction on the IUCN Red List of Endangered Species (Marshall et al, 2011). In 2014, Indonesia protected both manta ray species within their entire exclusive economic zone (an area of over 6 million km2) through the Ministerial Decree of Marine Affairs and Fisheries No 4/2014 (Ministry of Marine Affairs and Fisheries, 2014), in the hopes of slowing population declines. Limited information is available for Indonesian manta ray populations to assist in tracking the current status of these slow-growing species

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