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We performed an experiment to assess the proportion of time individual mud crabs spend active vs hiding in refuge in the presence of predator odor cues from either a single toadfish, a single blue crab, or control conditions with no predator cue. Previous work by Toscano et al. (2014) determined that differences in this behavior between individuals persist over months (i.e. the behavior defines the personality of individuals). We collected 300 mature mud crabs that were not missing any limbs (mean \u00b1 SD carapace width = 24.1 \u00b1 2.2 mm) by hand from intertidal oyster reefs within the North Inlet National Estuarine Research Reserve (33\u00b020\u2019N, 79\u00b010\u2019W, Georgetown, South Carolina). Crabs were collected in three cohorts of ten individuals during each of 10 blocked sampling periods (i.e., each blocked trial consisted of 30 crabs total). Individuals were randomly selected from 1 m2<\/sup> plots to ensure that natural cohorts of ten crabs were measured. Crab gender was identified by examination of the telson (167 males, 133 females).<\/p>\n Crabs were starved for 24 h and the carapace of each was marked with a unique nail polish (Sonia Kashuk) design to identify individuals. Preliminary work determined that these markings did not alter crab behavior. Cohorts were randomly assigned a predator cue treatment and placed into one of three separate flow-through mesocosms (circular with diameter 1 m; water height 15 cm). Each mesocosm contained ~2 cm sediment under a ~8 cm matrix of cleaned oyster shells covering the entire tank bottom. Thirty scorched mussels were distributed in three mesh containers within each mesocosm outside the reach of crabs to continuously stimulate foraging behavior [20]. Flow-through mesocosms were supplied with water from the estuary which was first pumped through a head tank. The head tank for each mesocosm contained either a mature toadfish (caudal length \u00b1 SD = 28.4 \u00b1 2.8 cm), blue crab (carapace width \u00b1 SD = 14.8 \u00b1 0.6 cm), or no predator depending on the predator odor cue treatment. Predators were caught from the estuary by dip net no more than one week prior to the experiment and fed mud crabs each day to ensure kairomones were produced. We conducted all experimental trials at night under red light following the observational procedures of Griffen et al. (2012) and Toscano et al. (2014) \u00a0to ensure mud crabs were at their most active and were undisturbed by the observer.\u00a0<\/p>\n Crabs were tested in trials consisting of one cohort per treatment (toadfish, blue crab, no predator) with six days separating the commencement of each trial. All trials began between the hours 2000-2100, and once cohorts were placed in the mesocosms, crabs were given 10 minutes to acclimate. After acclimating, we recorded whether crabs were actively exposed on the surface of the shell layer or were taking refuge underneath the shells at six minute intervals for the next three hours. The proportion of these 30 observations in which crabs hid in refuge and were not visible to the observer was used as our response variable.<\/p>\n Immediately after observing crab behavior (described in the last subsection), we used the same crab cohorts to assess whether crab predation risk was influenced by the proportion of time individual crabs spend in refuge within oyster shells and by predator species. We assigned crabs the same predator treatment they experienced previously to keep cohorts intact throughout the entire study.\u00a0 Crabs were fed a satiating amount of fish (Fundulus heteroclitus<\/em>), marked with individually-numbered bee tags (queen marking kit: the Bee Works, Orillia, Ontario, Canada), and starved for 24 h. After the starvation period, the cohorts were placed into one of three large flow-through mesocosms (diameter 2m; water height 90 cm). Each mesocosm contained ~ 2 cm of sediment underneath four clusters of live oysters (length ~38 cm, width ~31 cm, height ~28 cm) which were standardized by weight (15.000 kg within <0.1 %). Oysters were collected from the estuary and cleaned of any inhabiting crabs. Scorched mussels naturally attached to these collected oysters were standardized by number of individuals (within 8.3 %) and served as the mud crabs\u2019 food source to mimic natural conditions.<\/p>\n During each blocked trial (n=10), a single toadfish, blue crab, or no predator (to serve as a control for cannibalism) was placed in each mesocosm depending on the experimental treatment. We used the same individual predators which provided odor cues in the previous behavior experiment as predators within the large mesocosms. Predators were starved 24 h to standardize hunger levels and placed in the mesocosms 10 minutes prior to the mud crabs to ensure kairomones were distributed throughout the tank (no crabs were lost to predation during introduction into the tanks). Mud crab survival was checked daily for seven consecutive days to determine which individuals were consumed.\u00a0 This was done by removing all the oyster clumps and thoroughly raking the sediment. Any missing crabs were presumed dead as there was no way for crabs to escape and remnants of missing animals were often found.<\/p><\/div>","@type":"rdf:HTML"}],"http:\/\/ocean-data.org\/schema\/hasBriefDescription":[{"@value":"Mortality of crabs when exposed to either a single blue crab, toadfish, or no predator for a week.","@language":"en-US"}],"http:\/\/purl.org\/dc\/terms\/description":[{"@value":" Related Reference:<\/strong><\/p>\n Belgrad, B. and B. Griffen. 2016. Predator-prey interactions mediated by prey personality and predator hunting mode. Proc. Roy. Soc. B<\/em>: 283: 20160408. http:\/\/dx.doi.org\/10.1098\/rspb.2016.0408<\/a>.<\/p>\n Related Datasets:<\/strong><\/p>\n P. herbstii personality data<\/a> We assessed whether crab mortality was influenced by the fixed effects of crab refuge use (measured in the first experiment), predator species, and crab size using a mixed-effects Cox proportional hazards model (i.e., a survival analysis) with trial as a random effect (R package: frailtyHL). This model allowed us to right censor the data to account for crabs that were not consumed by the end of the trial. A Cox proportional hazards analysis is a statistical model which recognizes that the highest values\u00a0 in a study may simply be the maximum possible value because a result did not occur by the end of the observation period, so the model weighs the data points accordingly (i.e. the data are right censored). We also conducted a two-sample Kolmogorov-Smirnov test to compare the distribution of mud crab personality types consumed by blue crabs and toadfish.\u00a0<\/p>\n Statistical software: R, version 3.0.3 (R Development Core Team, Auckland, New Zealand; R Package frailtyHL<\/em> v. 3.0.3)\u00a0<\/p>\n BCO-DMO Processing:<\/strong><\/p>\n - added conventional header with dataset name, PI name, version date, reference information
P. herbstii predator behavior data<\/a><\/p><\/div>","@type":"rdf:HTML"}],"http:\/\/www.w3.org\/2000\/01\/rdf-schema#label":[{"@value":"P. herbstii mortality data","@type":"xsd:string"}],"http:\/\/ocean-data.org\/schema\/hasProcessingDescription":[{"@value":"
\n- renamed parameters to BCO-DMO standard
\n- changed month names to numbers
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