Taxonomic composition, abundance and habitat associations of squid paralarvae in the northern Gulf of Mexico
Introduction
Pelagic cephalopods, primarily squids, are dominant prey for several marine organisms, including migratory pelagic fishes (i.e. billfishes, tunas, and sharks), sea birds, and marine mammals (Clarke, 1996; Logan et al., 2013; Rodhouse et al., 2013; Staudinger et al., 2013). Squids are voracious predators as well and are essential components in open-ocean food webs, transforming biomass of micronekton into high-energy food for large predators (Clarke, 1996). It has been estimated that the yearly consumption of squids by sperm whales alone is greater than the total world catch of all marine and freshwater organisms combined (Clarke, 1977, as cited in Hoving et al., 2014). Squids occupy a large range of trophic levels, even exhibiting significant top-down control on their prey; however, as an important prey to large pelagic predators, open-ocean squids are constrained to a bottom-up control on their predators and can be regarded as keystone species in pelagic ecosystems (Coll et al., 2013). In fact, squid populations are increasing as predation and competition is reduced due to overexploited fish stocks (Caddy and Rodhouse, 1998).
Squids grow rapidly, have short lifespans (usually <2 years), and are semelparous, resulting in a fast life-history strategy (O'Dor and Webber, 1986). While this life strategy allows squids to be opportunists and take advantage of favorable environmental conditions, sudden deterioration of the environment or food sources can cause rapid declines in abundance and result in pronounced interannual variation in population sizes (Rodhouse et al., 2014). Despite these fluctuations, recent studies suggest that cephalopod populations are steadily increasing over time due to oceanic environmental changes (Doubleday et al., 2016). Still, cephalopod population dynamics are poorly understood and difficult to forecast due to their adaptability to changing conditions and opportunistic life history traits (Rodhouse et al., 2014; Doubleday et al., 2016). An improved understanding of squid abundance and habitat associations based on environmental factors during the pelagic paralarval stage is critical to population modeling efforts because recruitment variability is commonly linked to early life events (Cowen et al., 2000).
Little is known about the early life ecology of pelagic squids in the northern Gulf of Mexico (Gulf), which is a region that maintains some of the most productive fisheries in the United States (Chesney et al., 2000). The influences of the Mississippi River and mesoscale features, such as the Loop Current and associated eddies, provide nutrient rich habitats that increase primary and secondary production (Govoni et al., 1989; Biggs, 1992). Further, the northern Gulf is also recognized as an important spawning and nursery habitat for several large pelagic predators that are known to feed heavily on cephalopods, including billfishes, tunas, and cetaceans (Rooker et al., 2012; Ruiz-Cooley et al., 2012; Kitchens and Rooker, 2014; Judkins et al., 2013; Cornic et al., 2018). The purpose of the present study is to use a generalized additive modeling framework to characterize early life habitats of squids and to identify influential environmental parameters that affect their relative abundance and distribution in this basin.
Section snippets
Sample collection
Squid paralarvae were collected during annual plankton surveys conducted in shelf, slope, and open-ocean stations of the northern Gulf from approximately 27.0 to 28.0oN latitude and 88.0 to 91.0oW longitude. The 48 sampling stations were divided between two transects at 27.0oN and 28.0oN, with stations spaced approximately 15 km apart along each transect (Fig. 1). Plankton surveys have been conducted in this region from 2005 to 2017 due to its proximity to the Mississippi River, the
Results
A total of 613 squid paralarvae was collected over the three-year sampling period, encompassing 12 families (Table 1). The majority were small, with an average ML of 2.4 mm.
(±2.2 mm SD). Due to small size (<1.5 mm ML) or damage from the net, 288 squid paralarvae could not to be visually identified to family level. The most abundant family was Ommastrephidae with 108 individuals, accounting for 33% of paralarvae identifiable to family level for all three years combined. The next most abundant
Discussion
Squid paralarvae were broadly distributed over the sampling area, implying that the northern Gulf is a well-mixed system and may be an important spawning area. During the three-year study, squid paralarvae were present in over 76% of the stations sampled with mean densities per survey ranging from 3.5 to 17.1 paralarvae 1000 m-3. Due to varying sampling methods, comparing abundance to other studies is difficult; however, observed densities of this study are similar to values reported for
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgements
This research was made possible by a grant from the Gulf of Mexico Research Initiative. Data are publicly available through the Gulf of Mexico Research Initiative Information and Data Cooperative (GRIIDC) at https://data.gulfresearchinitiative.org (doi: 10.7266/N76W98G7, doi: 10.7266/N76M356C, and doi: 10.7266/n7-zs50-v228). We would like to thank staff and students of the Fisheries Ecology Laboratory at Texas A&M University at Galveston (especially J. Lee, C. Meinert, C. Steffens, and B.
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