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Linda L. Stehlik1*, Beth A. Phelan2, John Rosendale3, and Jonathan A. Hare4

1, 2, 3. Northeast Fisheries Science Center
National Marine Fisheries Service, NOAA
James J. Howard Marine Sciences Laboratory
74 Magruder Road
Highlands, New Jersey 07732

4. Northeast Fisheries Science Center
National Marine Fisheries Service, NOAA
Narragansett Laboratory
28 Tarzwell Drive
Narragansett, RI 02882
*Corresponding author: Tel. 732-872–3081; Email: Linda.Stehlik@noaa.gov

STEHLIK L. L., PHELAN, B. A., ROSENDALE, J., and HARE, J. A. 2015. Gastric evacuation rates in male Clearnose Skate (Leucoraja eglanteria) in the laboratory. J. Northw. Atl. Fish. Sci., 47: 29–36. https://doi.org/10.2960/J.v47.m700



Evacuation rates were determined for Clearnose Skate (Leucoraja eglanteria), an important predator in the mid-Atlantic United States shelf ecosystem. Male Skates (570–730 mm total length) were fed Sand Lance Ammodytes sp. and allowed to digest from 2–48 hr at two different temperatures. At selected times, fish were removed from tanks, sedated with tricaine methanesulfonate, and subjected to gastric lavage. This procedure was successful at removing the food from the stomachs without injury to the fish. Evacuation rates for the two temperature treatments were fit best by exponential models. The evacuation rates, per hour, were faster at 20°C than at 15°C, resulting in empty stomachs by 24 hr at 20°C, and 48 hr at 15°C. Evacuation rates at these temperatures were estimated as 0.102 and 0.059 proportion stomach contents per hour at 20oC and 15°C. These evacuation rates and their temperature dependence are similar to that of other species of elasmobranchs and some teleosts. Evacuation rates are often combined with stomach content data to estimate consumption. The results of this study indicate that evacuation rates by some skates may be up to five times higher than currently used in multi-species and ecosystem models of the Northeast U.S. Shelf. The implication is that consumption may also be higher, highlighting the need for more research to increase the accuracy in evacuation rates estimates.

Keywords: digestion, evacuation, consumption, multispecies modeling, ecosystem modeling, elasmobranchs, skates


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The importance of skates in the trophic dynamics of the Northeast U.S. Shelf Ecosystem has been changing. Initially, Link et al. (2002) reported that predation by elasmobranchs (1973–1998) had little effect on groundfish numbers or biomass. However, there has been a biomass shift from groundfish to elasmobranchs and crustaceans during the last two decades (Lucey and Nye, 2010), that indicates skates are now among the dominant predators in the shelf ecosystem (Link and Sosebee, 2008; Smith and Link, 2010). Seven species of the family Rajidae are common in the Northeast U.S. continental shelf ecosystem, occupying a variety of depths and temperature ranges (Gabriel, 1992). Clearnose Skates (Leucoraja eglanteria) are among the top 50 demersal species by biomass caught on the Northeast Fisheries Science Center (NEFSC) spring and autumn bottom trawl surveys (Lucey and Nye, 2010) but are more common summer residents south of Cape Cod, Massachusetts and are frequently caught in Mid-Atlantic coastal bays (Wilk et al., 1998; Packer et al., 2003). Large Clearnose Skates (>61 cm; sexes combined), consume approximately equal proportions of benthic invertebrates, various benthic fishes, and Loligo squid (Packer et al., 2003; Link and Sosebee, 2008; Smith and Link, 2010). In some areas of the Mid-Atlantic, the proportion of teleosts in the diets of Clearnose Skates approaches 50% (Woodland et al., 2011).

To evaluate the importance of Clearnose Skates as predators in the ecosystem, estimates of biomass and consumption rate are needed (see Elliott and Persson, 1978, Durbin et al. 1983). Estimates of biomass can be derived from the Northeast Fisheries Science Center bottom trawl survey. Consumption can be estimated from stomach content data and knowledge of the rate at which food passes into the intestine (termed evacuation rate, Bromley, 1994). There is a relatively large amount of stomach contents data from fish in the Northeast U.S. Shelf Ecosystem (Smith and Link, 2010). Food habit information and consumption rates are used in multispecies models and stock assessments to more accurately predict interactions between species such as groundfish and elasmobranchs. Currently, consumption rates are estimated based on information known for other species or regions (Overholtz and Link, 2007) and there is relatively little system-specific information on how rapidly the food is evacuated, or how evacuation rate is affected by temperature. Rate of evacuation and the shape of the evacuation function depend on various factors including temperature, the fish’s metabolism, meal size, and the prey’s structure, such as soft tissue, exoskeleton, or bone (Fänge and Grove, 1979; Bromley, 1994; Nelson and Ross, 1995).

Our main objective was to determine the evacuation rates of Clearnose Skate, from the Mid-Atlantic region, under controlled laboratory conditions. To measure evacuation rates, we used gastric lavage, which allows one to determine the proportion of stomach contents remaining without sacrificing the fish (Kamler and Pope, 2001; Waters et al., 2004; Wanner, 2006). We believe this information, along with that already determined for Little Skate and Winter Skate (Nelson and Ross, 1995; Wunder, 1995), will help provide more accurate consumption information for skates in general and that this information will help improve stock assessments and multispecies models in the region.

Materials and Methods

Clearnose Skates (570–730 mm total length, 935–1650 g) were collected by otter trawl on three fishing trips 5–10 km off the coast of New Jersey in the last half of August 2013. Water temperature at the nearby Ambrose Buoy averaged 22.3oC over the period of collection (National Climatic Data Center, NOAA). Tow times were <5 minutes, and the captured skates were held in an onboard live-well that received regular changes of seawater. Upon arrival at the dock, the skates were transferred to 64 gallon coolers and transported to the laboratory within 20 minutes. Only male Clearnose Skates were captured.

In the laboratory, skates were maintained in holding tanks (2.5 m diameter; 0.5 m depth) without sediment that received flow-through water from Sandy Hook Bay (salinity 25–26 psu, temperature 20–21°C). The light cycle was maintained at a constant 12 hr light and 12 hr dark. Skates are commonly collected from the Hudson-Raritan estuary at these temperatures and salinities during the late summer (Packer et al., 2003). Before experiments commenced, all tanks were gradually decreased in temperature to 20oC ±1.0°C, using a mixture of ambient estuarine water and additions of chilled or heated estuarine water. When experiments at 20°C were completed, all tanks including the holding tanks were gradually decreased to 15oC. Fish were fed a maintenance ration every other day of thawed Sand Lance (Ammodytes sp.) or Silverside (Menidia sp.) ad libitum. Most skates responded immediately to the presence of food, actively searched the bottom, and consumed the Sand Lances whole. Only fish that ate consistently and showed no external abrasions or injuries were used in experiments. The total number of skates used in experiments was 27.

For each evacuation experiment, eight skates at a time were measured, weighed, tagged, and transferred to individual 1.8 m diameter round tanks. In the first series of experiments, all tanks were maintained at 20°C (±1.0°C), and in the second series, 15°C (±1.0°C). Fish were allowed to reacclimate for one to two days after transfer, and were starved one to two days before each trial. Each skate was then offered four weighed whole Sand Lance, and if those were consumed, another four were weighed and offered. Skates were allowed to feed for 30 min, and then uneaten food was removed, weighed, and subtracted from the amount given. Skates that fed were randomly selected for gastric lavage at different digestion times.

Clearnose Skates that consumed one or more Sand Lances were used for pulsed gastric lavage (Kamler and Pope, 2001). Individual skates were sedated in a cooler containing 20 l of water from their own tanks and 1 g tricaine methanesulfonate. A skate was considered sedated when it could not right itself after being turned over, yet continued to respire. The skate was then removed from the cooler by hand and held ventral side up above a tray, while a hand-pumped compression sprayer nozzle was inserted through the esophagus and into the stomach. A stream of seawater from the sprayer reservoir was gently and intermittently pumped into the stomach, lavaging the contents out of the stomach. Lavage was stopped when no more visible material from the stomach was seen and the water expelled was clear. The skate was then returned to its tank and allowed to rest for a minimum of two days. Skates that did not eat in the experimental tanks were removed and replaced with other skates from the holding tanks. Skates that did feed were only subjected to four lavages before they were removed from the experimental tanks and returned to the holding tanks. A few skates were dissected after lavage to confirm the efficiency of the procedure.

The evacuate was sieved through 1 mm mesh, drained, scraped onto a damp paper towel, and then weighed (wet weight). Mucous, a product of the digestive system, significantly delayed drainage but error was no more than 0.5 g per stomach, determined by comparison of the weight of an empty wet sieve to the weight of a sieve scraped free of as much mucous as possible.

Evacuation rate, expressed as proportion lost from the stomach per hour, was estimated by statistically modeling percent weight of prey remaining in the stomach by time. Proportion remaining (WP) was calculated by dividing the stomach content weight at the time of sampling (Wt) by the total weight of prey presented to each individual. Evacuation rate was then estimated as the loss of proportion stomach weight over time. Many authors conclude that models of evacuation rate with an exponential curve are most apt for carnivorous teleosts, and that linear or square root models are best for elasmobranchs, depending upon prey type (Fänge and Grove, 1979; Durbin et al., 1983; Nelson and Ross, 1995). Owing to this uncertainty, we fit both a linear (1) and an exponential (2) model.

WP=W0 - Rt   (1)


WP=W0e-Rt   (2)

where WP is the proportion remaining, t is the time of sampling, W0 is an estimated parameter of the proportion of the meal that enters the stomach, and R is an estimated parameter of the evacuation rate per hour. W0 is often less than 100% owing to the initial expression of liquid from the prey (Olson and Boggs, 1978).

Bromley (1988, 1994) suggested that exponential models of proportion stomach content data are misleading and that evacuation in most species is actually linear. At later hours of digestion, some stomachs with zero contents are found; because proportion stomach content cannot be less than zero these data are in effect censored. To evaluate this assertion we fit equation 1 using linear least square (lm function in R) and equation 2 using several statistical fitting procedures: non-linear least squares (nls function in R), ln transformed linear least squares (lm function in R), a general linear model with Gamma distribution and log link (using the glm function in R), and a beta regression with a log link (using the betareg function in R) (R CoreTeam, 2014; Cribari-Neto and Zeileis, 2014). These statistical techniques offer a modern approach to that used by Bromley (1988). Models were compared using AIC and r2, but direct comparison of all the models was not possible because of the different transformations and estimation procedures. To avoid errors with log-transforming observations of 0 stomach contents at specific times, it was assumed that 0.01 of the original contents remained.

Evacuation rate decreases with decreasing temperature (Durbin et al., 1983) following an exponential model,

R=aebT  (3)

where a and b are parameters of the exponential model, T is temperature, and R is evacuation rate. This model was fit using the two estimates of evacuation rate at the two temperatures. We recognize that this model was fit with two data points only. Our purpose is simply to estimate the parameters a and b and compare these parameters to other studies that have estimated evacuation rates in skates.


During the 20°C experiments, gastric lavage was performed 47 times. Randomly selected skates were lavaged at 2, 4, 5, 6, 8, 9, 12, 20 and 24 hrs (Fig. 1a). Skates were observed to eat from 1 to 11 Sand Lances during 30 min. Meal sizes ranged from 2.4 to 51.8 g (mean 23.0 g) averaging 1.73% of body weight, (0.20% to 3.2%). Evacuation of the stomachs of Clearnose Skates, or the presence of <5% of the food given, was complete by 24 hr at 20°C (Fig. 1a).

During the 15°C experiments, gastric lavage was performed 28 times. Randomly selected skates were lavaged at 4, 5, 20, 24, 28, and 48 hrs (Fig. 1b). Skates were observed to eat only from 1 to 7 Sand Lances during 30 min. Meal sizes ranged from 4.7 to 34.8 g (mean 19.2 g) averaging 1.39% of body weight (0.39% to 3.81%) (n = 28). Complete evacuation of the stomachs, or the presence of <5% of the food given, occurred by 48 hr at 15°C (Fig. 1b). After the lavage procedures, the skates recovered from sedation within 10 or 15 minutes. No observable negative effects were seen from lavage or sedation.

The exponential model (Eq. 2) fit the data better than the linear model (Eq. 1) comparing both AIC and r2 values (Table 1). The various approaches to fit the exponential model all yielded similar results (Table 1, Fig. 2). Based on the nonlinear fit of the exponential model, gastric evacuation rates were 0.102 at 20°C and 0.059 at 15°C. The estimates of evacuation rates in this study are comparable with estimates made for other Leucoraja species (Table 2 and Fig. 3).

The model of temperature dependence (R=aebT) estimated a = 0.011 and b = 0.109 (Fig. 4). These parameters should be viewed cautiously as only two temperatures were used in their estimation. However, the b term of the temperature dependence model was comparable to estimates for teleosts: Elliott (1972) estimated b = 0.112 and Durbin et al. (1983) estimated b = 0.111 (Fig. 4). The a term for Clearnose Skates was lower than that for teleosts: Elliott (1972) estimated a = 0.053 and Durbin et al. (1983) estimated a = 0.041. These functions we determined are higher than what is used in many regional multispecies models (e.g. Link and Sosebee, 2008) and suggest some phylogenetic concurrence in evacuation rate among skates (Fig. 4).


We found that gastric lavage works well in Clearnose skates and they are very good laboratory animals. Skates have simple stomachs with an open esophagus and a sphincter at the posterior end, so lavage efficiently washes out the stomach’s contents. Wunder (1995) also found that gastric lavage was very effective on Winter Skates with piscine or crustacean prey.

Bromley (1988, 1994) concluded that exponential evacuation rate models could be misleading and that evacuation in most species of fish is actually linear. Our evaluation of the linear model did not support Bromley’s (1988) assertion. However, there are a number of modern statistical approaches that allow non-normal data distributions to be modeled. The Gamma distribution assumes values are positive (0 to ∞) and the Beta distribution assumes values ranged between 0 and 1. A statistical evaluation of the different methods is beyond the scope of this paper, but all the approaches for fitting the exponential model yielded similar results and fit the data better than the linear model.

Evacuation rates derived here for Clearnose Skate are similar to those estimated for other Leucoraja skates when the exponential models are compared. Skates of the genus Leucoraja have similar body shapes, food search behaviors, and possibly comparable activity levels and metabolic rates. When fed small fish, all three species studied to date (Little Skate, Nelson and Ross, 1995; Winter Skate, Wunder, 1995; Clearnose Skate, this study), exhibited rapid commencement of digestion and some variability in rates of digestion among individuals. Although Nelson and Ross (1995) found the best fit for evacuation of Sand Lance at 10° by Little Skate was the square root model, in our study, the exponential model best described the evacuation rates in Clearnose Skates at both temperatures. Studies with Winter Skate indicate that crustaceans may be evacuated more slowly than fish (Wunder, 1995) and this result is also found in other studies (see Durbin et al., 1983). Curvilinear functions better described the evacuation of shrimp by Winter Skate due to a delay in commencement of digestion (Wunder, 1995). Age of the fish, stage of sexual development, mode of ingestion, and structure of the prey also contribute to rapidity of digestion. In this experiment, we reduced variability in evacuation rates from confounding factors by using only one food type and only male skates above a minimum size.

Temperature had a significant effect on evacuation in Clearnose Skate; the evacuation rate was higher at 20°C than 15°C. Temperature has a major influence upon digestion rates due to its effects on biochemical reactions, and evacuation rates increase as temperature increases (Durbin et al., 1983). When temperature was increased, evacuation rate also increased in other skates (Nelson and Ross, 1995; Wunder, 1995). Comparing among the three skate species studied to date indicate a similar temperature dependence in evacuation, but a greater number of species will need to be studied to verify interspecific similarities and differences.

The impact of consumption by elasmobranchs upon prey species in the Northeast U.S. Shelf Ecosystem may be substantial. Estimates for total consumptive demand by Clearnose Skate ranged between 2 000 and 18 000 mt/year during the 2000s (Link and Sosebee, 2008). Clearnose Skate is among the top 50 species caught in NEFSC bottom trawl surveys from 1968–2006, though less in biomass than Winter (Leucoraja ocellata), Little (L. erinacea), and Thorny Skates (Amblyraja radiata) (Lucey and Nye, 2010). The seven northeast U.S. skate species currently are managed together as a complex, but because each species has a particular thermal range and life history (Hogan et al., 2013), they may be managed separately in the future. Clearnose Skates are unique in that they are a warmer-water species and more abundant in the Mid-Atlantic Bight (Woodland et al., 2011).

Skate consumptive removals are a means to add ecological considerations to stock assessments and multi-species food web models (Link and Sosebee, 2008). Results of this study for Clearnose Skate and those of Little and Winter Skate can be used to develop a general evacuation rate function for skates or to reestimate overall consumption by skates in the ecosystem. Consumption is typically estimated as a function of mean stomach content weight and evacuation rate (Durbin et al., 1983). In the Northeast U.S. Shelf Ecosystem, decades of field work have been conducted to quantify stomach contents in multiple species (Smith and Link, 2010), yet relatively few estimates of evacuation rate have been generated (Fig. 4). A greater emphasis should be given to estimating evacuation rates for additional species with an evaluation of Order or Family-level concurrence in evacuation rates. Further, a review of evacuation rates is also warranted. Newly measured evacuation rates and a synthesis of past work could be used to improve upon the sub-class-level estimates typically used in multispecies models in the region (Overholtz and Link, 2007; Link et al., 2008).


We thank John Manderson, Jeffrey Pessutti, Pete Plantamura, and other personnel of the NOAA James J. Howard Marine Sciences Laboratory, and Mike Fogarty and Brian Smith of the Food Web Dynamics Program at the Woods Hole Laboratory. Thanks also to reviewers who suggested improvements to the manuscript.


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Citation: STEHLIK L. L., PHELAN, B. A., ROSENDALE, J., and HARE, J. A. 2015. Gastric evacuation rates in male Clearnose Skate (Leucoraja eglanteria) in the laboratory. J. Northw. Atl. Fish. Sci., 47: 29–36. https://doi.org/10.2960/J.v47.m700
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