These methods, instrumentation and/or protocols apply to all data in this dataset:Methods and protocols used in the collection of this data package |
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Crab surveys were conducted following the protocol developed by McMahan (2020). Surveys took place in the lower third of the intertidal zone, during negative or zero tides. Most surveys occurred between May and November during the height of productivity in the intertidal zone. From 2018-2021, surveys were conducted monthly from May through November, as effort allowed. Beginning in 2022, surveys were conducted three times on a seasonal basis: spring (April or May), summer (July or August), and fall (October or November). All surveys sites were wave-sheltered rocky intertidal areas with cobble (i.e., not stable, rolled by wave action) and algal canopy habitat with at least 100 m of shoreline to accommodate the sampling. At each site, the same 100 m section was surveyed on every sampling trip; these areas were delineated by permanent landmarks. Surveys were conducted by haphazardly tossing a 1 m2 quadrat within the predefined low intertidal zone area running parallel to the shoreline. A visual estimate of the percent of both moveable rock (i.e., cobble/gravel that you can look underneath) and algae canopy cover (e.g. Ascophyllum or Fucus spp.) within the quadrat to the nearest quarter percent (i.e., 0, 25, 50, 75, or 100%) was made. As the rocky intertidal habitat is often patchy and can contain areas of sand, mud, ledge, or other habitats where green crabs are not found, only quadrats with greater than 50% movable rock, or greater than 50% algal canopy were surveyed. Within each quadrat, rocks and cobble were lifted, and algae was moved aside to look for crabs. Data recorded for each crab included species identification, carapace width (widest part of the carapace, spanning from tip to tip of the terminal spines) measured to the nearest 1 mm, sex, number of claws, number of legs, shell condition (i.e., hard- or soft-shell as determined by whether the carapace resists (hard) or gives (soft) when finger pressure is applied), and the presence (i.e., ovigerous) or absence of extruded eggs for females. For green crabs only, shell condition was also identified if pre-molt, as the timing of the green crab molt cycles are of particular interest to the emerging soft-shell green crab fishery. Color was also recorded for green crabs using the protocol developed by Young and Elliot (2017). All crabs were returned to the habitat and any cobble or algae that was moved was replaced.
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Bibliography
McMahan 2020 Green Crab Protocol:
McMahan, M. D. (2020). Assessing Intertidal Populations of the Invasive European Green Crab. JoVE (Journal of Visualized Experiments), 163, e61667. https://doi.org/10.3791/61667
Green Crab Color Chart:
Young, A. M., Elliott, J. A., Incatasciato, J. M., & Taylor, M. L. (2017). Seasonal catch, size, color, and assessment of trapping variables for the European green crab Carcinus maenas (Linnaeus, 1758) (Brachyura: Portunoidea: Carcinidae), a nonindigenous species in Massachusetts, USA. Journal of Crustacean Biology, 37(5), 556–570. https://doi.org/10.1093/jcbiol/rux068
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