INTRODUCTION
The spreading of invasive species across marine ecosystems has had extreme effects on regional biodiversity and production of fishery resources (Green et al. 2012, Albins and Hixon 2013). The invasion of the Indo-Pacific lionfish Pterois volitans (Linnaeus 1758) across the western Atlantic and the Caribbean has produced detrimental effects on native species. In the Bahamas, this species reduced the biomass of 42 small-bodied fish species by 65% in 2 years (Green et al. 2012). The success of P. volitans is partly attributed to its voracity, varied diet, and high consumption rates (Morris and Akins 2009, Layman and Allgeier 2012). In its native range the lionfish, a reef fish, feeds primarily on small fishes and invertebrates (Harmelin-Vivien and Bouchon 1976); however, in invaded ranges the lionfish has been reported to exhibit opportunistic behavior, as it has been found in unexpected locations, such as temperate coasts (Aguilar-Medrano 2017) or mangroves (Barbour et al. 2010), showing opportunistic generalist diets largely based on bony fishes and crustaceans (Morris and Akins 2009, Layman and Allgeier 2012) and some mollusks (Arredondo-Chávez et al. 2016).
Since P. volitans was first reported in the Veracruz Reef System National Park (VRSNP) in 2012 (Santander-Monsalvo et al. 2012), local authorities have been reporting its presence in the park. Despite ongoing reports and with the exception of the study by Montoya-Mendoza et al. (2017), who analyzed the parasites of P. volitans in this area, no studies on the biology of the species in this new environment have been published. Therefore, in order to produce novel information on P. volitans, the present study tested sampling at different depths and times on a silt flat south of the VRSNP with a fishing gear that allowed collecting representative samples of all sizes. The objectives of this study were (1) to report new distribution records of P. volitans in the Gulf of Mexico, (2) to document the feeding habits of collected specimens to better understand the impact P. volitans may have on the native community, and (3) to determine if there was any variation in the diet of specimens with size and weight.
MATERIALS AND METHODS
Sampling design
Five stations located along the coast of Veracruz, south of the VRSNP, were sampled in March 2018 (Fig. 1), covering latitudes from 20º38 N to 20º48 N, longitudes from 96º51 W to 96º 56 W, and depths from 45 to 71 m. All stations had a fine and thick silty substratum. Sampling was designed to test for different times in a day, with 2 samplings in the morning (station 4, 6:47 AM; station 2, 8:46 AM), 2 in the afternoon (station 1, 12:48 PM; station 3, 1:58 PM), and 1 at night (station 5, 8:00 PM). All samples were collected using a shrimp trawl net (18.3 m in length, 3.4 cm mesh size), which was towed for 20 to 30 min at a constant speed of 2.5 knots. The collected specimens were frozen and identified to species level (Schultz 1986, Labastida-Estrada et al. 2019).
Stomach content analyses
The feeding habits of specimens were determined by analyzing stomach contents. All specimens were measured (standard length, SL) and weighed (wet weight). The digestive tract of each specimen was removed and weighed, and stomach contents were all extracted and identified to the lowest possible taxonomic unit. The contribution of each prey taxon to the overall diet was assessed using 3 relative metrics. Of the three, the percent composition by weight takes into account the wet weight of each component, and the total weight of a food category is then expressed as a percentage of the overall weight of stomach contents (Vega-Cendejas et al. 1994). The percent composition by area was used when stomach contents were constituted of very small prey whose weight was not possible to record with an analytical balance; this method provides a more representative measure of biomass and can be applied to all food components (Canto-Maza and Vega-Cendejas 2007). The percent frequency of occurrence takes into account the number of times a prey appears in the stomach contents of a group of fish and is expressed as a percentage (Canto-Maza and Vega-Cendejas 2007).
Size, weight, and diet
Since the size and weight variables did not meet the normality criteria, we used non-parametric methods. The relationship between the SL and weight of specimens and the weight of the digestive tract was analyzed by Spearman’s D correlation (Press et al. 1992). Then, to make a size/weight group (SWG) classification, a cluster analysis based on the size and weight of specimens was performed by the unweighted pair group method with arithmetic mean (UPGMA) using the Euclidian distance. UPGMA is an agglomerative hierarchical clustering method that constructs a tree that reflects the structure present in a pairwise similarity matrix (Sokal and Michener 1958). The obtained grouping was analyzed via a permutational multivariate analysis of variance (PERMANOVA) to test for significant differences between 2 or more groups (Anderson 2001). PERMANOVA was also used to determine if there were differences in the diet across SWGs using the information gathered from prey items, such as occurrence, area, and weight. All statistical analyses were done using PAST 3.20 (Hammer et al. 2001).
RESULTS
A total of 17 specimens were collected, with SLs ranging from 6.9 to 40.2 cm and weights from 7.6 to 847.7 g. All specimens were confirmed as P. volitans (D: XIII-12, A: III-8). Most specimens were collected at station 5, the nocturnal sampling station (Table 1).
Depth (m) | ||||||||
Station | Latitude | Longitude | Initial | Final | Time | Specimen | FS (cm) | FW (g) |
1 | 20º43(8.28( | 96º51(23.64( | 71 | 71 | 12:48 PM | 1 | 6.9 | 7.62 |
2 | 20º38(39.36( | 96º52(11.04( | 57 | 61 | 8:46 AM | 2 | 17.5 | 189.30 |
3 | 21.0 | 320.00 | ||||||
4 | 22.3 | 241.20 | ||||||
3 | 20º39(23.10( | 96º55(22.68( | 46 | 45 | 1:58 PM | 5 | 31.0 | 418.30 |
6 | 40.2 | 847.70 | ||||||
4 | 20º41(13.38( | 96º56(16.02( | 45 | 43 | 6:47 AM | 7 | 40.3 | 847.60 |
5 | 20º48(16.68( | 96º55(33.90( | 63 | 67 | 8:00 PM | 8 | 10.2 | 17.63 |
9 | 18.6 | 81.73 | ||||||
10 | 18.6 | 106.62 | ||||||
11 | 21.9 | 135.20 | ||||||
12 | 23.2 | 160.03 | ||||||
13 | 25.0 | 201.10 | ||||||
14 | 27.0 | 269.40 | ||||||
15 | 28.6 | 297.50 | ||||||
16 | 29.4 | 424.90 | ||||||
17 | 38.0 | 831.10 |
Diet
Three main taxonomic groups were identified in the diet of P. volitans, the phylum Mollusca, the subphylum Crustacean, and the superclass Osteichthyes, being the bony fishes the dominant items (Table 2). Of the 32 classified items, 21 were bony fishes, 9 crustaceans, and 2 mollusks. The values for percent composition of prey ítems by area and by weight were highly similar; approximately 95.40% of the total composition by area and weight was made up of bony fishes, whereas crustaceans made up approximately 4.20% and mollusks approximately 0.36% of total composition (Table 2).
Group number | Prey Item | FO (%) | PA (cm2) | PW (g) | |
SWG1 (8 specimens) | Fish | Osteichthyes | 43.75 | 79.36 | 76.49 |
Synodontidae | 6.25 | 1.49 | 1.49 | ||
Serranus spp. | 6.25 | 9.40 | 13.94 | ||
Crustacea | Crustacea | 6.25 | 1.66 | 0.83 | |
Decapoda | 6.25 | 1.33 | 0.67 | ||
Farfantepenaeus spp. | 6.25 | 1.79 | 1.65 | ||
Portunus spp. | 6.25 | 3.10 | 2.41 | ||
Raninoides spp. | 6.25 | 0.60 | 0.11 | ||
Sicyonia spp. | 6.25 | 0.86 | 1.35 | ||
Mollusca | Bivalvia | 6.25 | 0.41 | 1.05 | |
SWG2 (6 specimens) | Fish | Osteichthyes | 50.00 | 38.55 | 19.23 |
Synodontidae | 8.33 | 2.91 | 2.48 | ||
Serranus spp. | 8.33 | 0.90 | 0.22 | ||
Scyacium gunteri | 8.33 | 56.01 | 77.02 | ||
Crustacea | Brachyura | 16.67 | 1.28 | 0.80 | |
Mollusca | Gastropoda | 8.33 | 0.36 | 0.24 | |
SWG3 (3 specimens) | Fish | Osteichthyes | 75.00 | 84.17 | 78.50 |
Crustacea | Sicyonia spp. | 25.00 | 15.83 | 21.50 | |
Total (17 specimens) | Fish | 65.63 | 94.96 | 95.88 | |
Crustacea | 28.15 | 4.69 | 3.75 | ||
Mollusca | 6.26 | 0.35 | 0.37 |
Size, weight, and diet
Correlation was strongest between the SL and weight of specimens (r = 76.5, P < 0.000), followed by the correlation between the weight of specimens and the weight of the digestive tracts (r = 146.5, P < 0.001) and the correlation between the SL of specimens and the weight of the digestive tracts (r = 238, P < 0.005). With data on specimen SL and weight, the UPGMA produced 3 statistically independent groups (F = 120.6, P < 0.000): SWG1, which grouped 8 of the smallest and lightest specimens (μ SL = 17.74 cm, weight = 112.4 g); SWG2, which grouped 6 specimens with mean size/weight (μ SL = 26.55 cm, weight = 328.55 g); and SWG3, which grouped 3 of the largest and heaviest specimens (μ SL = 39.47 cm, weight = 842.17 g). The comparison of frequency of occurrence, area, and weight between SWGs showed no significant differences (F = 1.275, P = 0.285; Fig. 2).
DISCUSSION
Our study corroborates the results of Morris and Akins (2009), Layman and Allgeier (2012), and Arredondo-Chávez et al. (2016), which indicate that the diet of lionfish in an invaded range is largely composed of bony fishes, crustaceans, and mollusks, although we found mollusks in the diet of only SWG1. In the diet contents of P. volitans, we found fishes belonging to the genus Serranus, which in this area comprises 6 reef-associated species, the fish species Scyacium gunteri, which is a bottom dweller unassociated with reefs (Robertson and van Tassell 2019), and hard-shelled organisms belonging to the infraorder Brachyura and the classes Bivalvia and Gastropoda. We did not find differences in the diets between SWGs; however, it was clear that SWG1 had the more diverse diet.
According to our study, the highest P. volitans density was found at station 5, the one closest to the VRSNP, which could indicate that the closer the area to the reef the higher the density. Station 5, however, was only sampled at night and the high density there could also just be a corroboration of the nocturnal habits of the lionfish (Myers 1991). Our results indicate low lionfish density in the study area, as we captured 1 to 10 specimens per station in each trawl, which covered an area of approximately 22,715 m2. In our study we tried testing the use of a shrimp trawl net with a small mesh size to capture lionfish specimens in a wide range of sizes. Although we achieved the objective, this methodology is useful only for flat bottoms, away from the reefs.
The experience during these years of the invasion of P. volitans in the Gulf of Mexico and the Caribbean made it clear that efforts must be directed to control lionfish populations, as eradication seems unfeasible (Albins and Hixon 2013). It is important to produce information that reveals how this species interacts within an ecosystem in order to propose effective plans to buffer its negative effects. Trophic data can help us anticipate its arrival by directing conservation efforts to protect the key species found in its diet. Trophic analyses can help determine vulnerable life stages given the specific dietary needs, and control efforts can therefore be more specific by focusing on those life stages. The present study was a first attempt to understand the relation between the size, weight, and diet of the invasive lionfish P. volitans on the southern coast of Veracruz, Mexico.