2013). Here

we present for the first time data on (1) the occurrence, distribution and density of R. harrisii in the Gulf of Gdańsk, (2) the structure of the benthic communities of which it is a component, and (3) preliminary characteristics of the individuals with regard GSK-3 inhibitor to sex and size. Based on material collected in 2006–2010, this study provides new information on this non-native species. Together with other ecological data (e.g. on food preferences and consumption rate), the results may find application, e.g. in ecological models, or be useful in the development of management strategies for the species. Samples were taken with a bottom dredge (33 × 66 cm, mesh size 0.5 × 0.5 cm) from r/v ‘Oceanograf 2’ at 129 randomly

chosen sampling points located at depths from 5 to 60 m. The dredging time of 5 min as well as the vessel’s speed of 1.5 knots were recorded to estimate the abundance of R. harrisii. In order to obtain information TSA HDAC clinical trial on seasonal variations in Harris mud crab abundance, material was also collected monthly from January to September (excluding May 2009) from two depth profiles located in Gdynia (G) and Sopot (S). Three sampling points were fixed at each profile. The same dredging procedure was repeated three times at each sampling point ( Table 1). At each sampling point temperature (± 0.1°) and salinity (± 0.1 PSU) were determined with a Multi340i multimeter (WTW, Germany). The macrobenthic taxa found in the sample were identified as accurately

as possible, based on Stańczykowska (1986), Żmudziński (1999), Kołodziejczyk & Koperski (2000) and Barnes (2005). The frequency of co-occurring taxa was determined at 46 random sampling points in Puck Bay (n = 17) and in the Gdynia and Sopot area (n = 29). Additional information on the occurrence of R. harrisii in shallow Sclareol waters (< 5 m) was obtained from divers and the local community. After collection, the animals were immediately frozen at − 20 °C. In the laboratory the crabs were sexed on the basis of their abdominal structure and pleopod shape (De Man 1892), and their carapace width was measured (± 0.01 mm) with slide calipers (ECOTONE, Poland). In accordance with Turoboyski (1973), specimens with a carapace width under 4.4 mm were classified as juveniles. The results were expressed as mean plus standard deviation (mean ± SD). The maps were prepared in the ArcGIS 8.x. program. In 2006–2010 Rhithropanopeus harrisii was recorded at 69 out of 129 sampling points, at depths from 0 to 20 m ( Figure 1a). In the samples from Puck Bay, which has a muddy bottom, gammarids were dominant among the organisms co-occurring with R. harrisii. Crangon crangon and Cerastoderma glaucum were recorded in more than 50% of samples containing the Harris mud crab ( Figure 2a).