40% and 3.98%, on average, of the total abundance and biomass respectively ( Figure 2b). As a member state of the European Union, Poland has been obliged to implement the Water Framework Directive. One of the main goals of this Directive is to achieve good water quality by 2015. The ecological and chemical state of waters should be assessed on the basis of monitoring measurements. Because of the lack of integral indicators for the trophic

status of brackish waters, the trophic state of the Vistula Lagoon waters in this study was evaluated based on methods developed for lakes. This was possible because the Vistula Lagoon is not a typical brackish water body: owing to the low rate of water exchange with the sea, the salinity is relatively low (average 3.7 PSU), so freshwater organisms can flourish. Information on biological parameters in Polish coastal waters (including the Vistula GSI-IX price Lagoon) is scarce and inconsistent. Therefore, the ecological state of these waters has been only roughly assessed, Ibrutinib molecular weight mainly on the basis of the knowledge of experts and existing monitoring programmes (Report… 2005). The physicochemical parameters measured confirm the eutrophic state of these waters, indicated in earlier studies of the Polish part of the Vistula Lagoon (Margoński & Horbowa 2003a,b, Bielecka & Lewandowski 2004). The average values of the parameters (TP, SD, Chl a, TN, TN:TP) measured in summer indicate that Vistula

Lagoon waters are eutrophic; TN is also an index of mesoeutrophy ( Kajak 1983, Zdanowski 1983). However, according to Vollenweider’s (1989) classification, the values of TP, SD and Chl Idelalisib cost a measured in spring and summer are characteristic of hypereutrophy; this was corroborated by the trophic state indices. According to Carlson’s classification (1977), the TSIs calculated on the basis of Chl a, TP and SD indicate eutrophy ( Figure 3a). TP values were very high: in all three years of measurements they were close to

those characteristic of hypereutrophy. The situation was similar in the case of Chl a in 2007 and 2009. Only the water trophic state assessment based on water transparency seems doubtful because of the intensive resuspension of particles from the sediments, which leads to a decrease in water transparency unrelated to the presence of phytoplankton. TSI is generally used for assessing the trophic state of lakes, so the indices determined for the Vistula Lagoon should not be compared with their values obtained for lakes ( Margoński & Horbowa 2003b). The analysis of the physicochemical parameters measured in the Vistula Lagoon waters according to both Zdanowski’s (1983) and Vollenweider’s (1989) classifications indicates a state of eutrophy. In spring and summer the concentrations of TP and Chl a were more than twice as high as the values indicative of hypereutrophy ( Figure 3b). Therefore, based on the OECD classification and the magnitudes of these concentrations we can state that the Vistula Lagoon waters are hypereutrophic.