Assessing the effect of recreational scallop harvest on the distribution and behaviour of foraging marine turtles
NAT A L I E WIL DERMANN,CHRIS T O PHE R S ASSO CHRISTIAN GREDZENS and MARIANA M. P. B. FUENTE S
Abstract The impact of fisheries on marine megafauna is widely known but most studies have focused on commercial fisheries, overlooking the effect of local recreational fisher- ies. This is particularly important for marine turtles in near- shore habitats that overlap with recreational fisheries. We assessed the effect of recreational scallop fisheries on the dis- tribution and behaviour of foraging marine turtles in the coastal waters of the upper Eastern Gulf of Mexico. Before and during the scallop season we quantified the density and overlap of marine turtles and vessels sighted, and satellite tracked four turtles to assess their distribution and behav- iour. The relative distribution of marine turtles sighted dur- ing the scallop season overlapped with 48%of the area most frequently used by harvesters, and marine turtle activity hotspots shifted between seasons. In addition, during the scallop season the home range size of individual turtles appeared to decrease, and turtles displayed frequent changes in travel speed and directionality.We hypothesize that such changes are probably related to the distribution and move- ment of vessels and the abundant presence of people in the water. Our study highlights the importance of considering recreational fisheries and their local effect on marine mega- fauna for informing future adaptive management practices. However, further studies are needed to quantify the direct and indirect impacts of recreational fisheries and to assess the degree of risk of associated activities to marine turtle populations.
Keywords Caretta caretta, Chelonia mydas, Eastern Gulf of Mexico, Lepidochelys kempii, marine turtles, recreational fisheries, scallop harvest, wildlife management
The supplementary material for this article is available at
https://doi.org/10.1017/S0030605318000182
Introduction
species (Crowder & Norse, 2008). Of particular concern is bycatch, the unintended capture of non-target organisms during fisheries operations, which is considered to be one of the most serious threats globally to long-lived marine megafauna such as marine turtles (Wallace et al., 2013). Further impacts from fisheries can occur from vessel traffic, which may affect the fitness of individuals, energy ex- penditure, changes in foraging activity, displacement and disturbance, and mortality (Hazel et al., 2007; Powell & Wells, 2011; Barrios-Garrido & Montiel-Villalobos, 2016). As a consequence, there has been substantial effort to evalu- ate and address the impacts of fisheries on marine mega- fauna (e.g. Zydelis et al., 2009; Lewison et al., 2014). Assessments of the interactions between sea turtles and
C
fisheries have focused mainly on commercial fisheries, with little attention to the effects of recreational fisheries (Powell & Wells, 2011; Altieri et al., 2012; Young et al., 2014). This is an issue as 12% of the world’s population fish recreationally (Cooke & Cowx, 2004). In the USA rec- reational fishing averaged over 73 million trips and c. 9 mil- lion users annually during 2007–2017 (NMFS, 2017). This may have substantial consequences, both direct and indir- ect, upon marine environments and species. The few studies conducted to date have shown that recreational fishing and related activities can have profound effects on animal popu- lations and coastal ecosystems, including depletion of fish populations and ecosystem collapse from trophic-level cas- cades (Cooke &Cowx, 2004; Altieri et al., 2012; Young et al., 2014). Recreational fisheries in marine environments are con-
NATALIE WILDERMANN,CHRISTIAN GREDZENS and MARIANA M. P. B. FUENTES (Corresponding author) Department of Earth, Ocean and Atmospheric Science, Florida State University, Tallahassee, FL 32306-4320, USA E-mail
mfuentes@fsu.edu
CHRISTOPHER SASSO National Marine Fisheries Service, Southeast Fisheries Science Center, Miami, Florida, USA
Received 23 October 2017. Revision requested 24 November 2017. Accepted 18 January 2018. First published online 3 July 2018.
centrated in coastal areas, which are also home to multiple species and populations of marine turtles. This is the case within the Big Bend Region of north-western Florida, which serves as important developmental habitat for green Chelonia mydas, Kemp’s ridley Lepidochelys kempii, and loggerhead Caretta caretta turtles (e.g. Schmid et al., 2003; Barichivich, 2006), and also supports Florida’s largest recre- ational bay scallop Argopecten irradians harvest. The scallop fishery occurs annually from late June to late September (Geiger et al., 2015), a period with water temperatures favourable for marine turtles (Schmid & Witzell, 2006).
Oryx, 2020, 54(3), 307–314 © 2018 Fauna & Flora International. This is a work of the U.S. Government and is not subject to copyright protection in the United States. doi:10.1017/S0030605318000182
ommercial, recreational and artisanal fisheries can have both direct and indirect impacts on threatened
Page 1 |
Page 2 |
Page 3 |
Page 4 |
Page 5 |
Page 6 |
Page 7 |
Page 8 |
Page 9 |
Page 10 |
Page 11 |
Page 12 |
Page 13 |
Page 14 |
Page 15 |
Page 16 |
Page 17 |
Page 18 |
Page 19 |
Page 20 |
Page 21 |
Page 22 |
Page 23 |
Page 24 |
Page 25 |
Page 26 |
Page 27 |
Page 28 |
Page 29 |
Page 30 |
Page 31 |
Page 32 |
Page 33 |
Page 34 |
Page 35 |
Page 36 |
Page 37 |
Page 38 |
Page 39 |
Page 40 |
Page 41 |
Page 42 |
Page 43 |
Page 44 |
Page 45 |
Page 46 |
Page 47 |
Page 48 |
Page 49 |
Page 50 |
Page 51 |
Page 52 |
Page 53 |
Page 54 |
Page 55 |
Page 56 |
Page 57 |
Page 58 |
Page 59 |
Page 60 |
Page 61 |
Page 62 |
Page 63 |
Page 64 |
Page 65 |
Page 66 |
Page 67 |
Page 68 |
Page 69 |
Page 70 |
Page 71 |
Page 72 |
Page 73 |
Page 74 |
Page 75 |
Page 76 |
Page 77 |
Page 78 |
Page 79 |
Page 80 |
Page 81 |
Page 82 |
Page 83 |
Page 84 |
Page 85 |
Page 86 |
Page 87 |
Page 88 |
Page 89 |
Page 90 |
Page 91 |
Page 92 |
Page 93 |
Page 94 |
Page 95 |
Page 96 |
Page 97 |
Page 98 |
Page 99 |
Page 100 |
Page 101 |
Page 102 |
Page 103 |
Page 104 |
Page 105 |
Page 106 |
Page 107 |
Page 108 |
Page 109 |
Page 110 |
Page 111 |
Page 112 |
Page 113 |
Page 114 |
Page 115 |
Page 116 |
Page 117 |
Page 118 |
Page 119 |
Page 120 |
Page 121 |
Page 122 |
Page 123 |
Page 124 |
Page 125 |
Page 126 |
Page 127 |
Page 128 |
Page 129 |
Page 130 |
Page 131 |
Page 132 |
Page 133 |
Page 134 |
Page 135 |
Page 136 |
Page 137 |
Page 138 |
Page 139 |
Page 140 |
Page 141 |
Page 142 |
Page 143 |
Page 144 |
Page 145 |
Page 146 |
Page 147 |
Page 148