The effects of ambient solar UV radiation (280 to 400 nm) were determined using 3 natural marine protist communities incubated in 650 l tanks (minicosms) for 13 to 14 d over the summer of [2002][2003] at Davis Station, Antarctica. Minicosms were exposed to ambient light that was variously attenuated to give treatments of photosynthetically active radiation (PAR, ≥385 nm wavelength), PAR + UV-A radiation (315 to 385 nm), and PAR + UV-A + 4 different treatments of UV-B radiation (280 to 315 nm) that simulated a range of equivalent depths (ED) in the water column from 4.43 to 7.15 m. Results showed a seasonal progression in the response of microbial communities to UV radiation exposure. The first experiment in November showed that the microbial community was significantly inhibited in the PAR + UV-A-exposed treatment but this inhibition declined with increasing addition of UV-B radiation. The second experiment in December showed that UV-A or UV-B radiation had few significant effects. Like in Expt 1, some taxa were inhibited by PAR + UV-A or promoted by UV-B, but most were inhibited at the highest UV-B irradiances (≤4.43 m ED). The last experiment in January showed UV-B induced inhibition of all but one of the dominant taxa. The seasonal transition in UV wavelengths responsible for inhibition of protists may be due to ozone reduction, the light history of protists, and/or changes in species composition. The increasing UV-Binduced inhibition we observed over the summer corresponded to a decline in ozone concentrations over Davis. This recurrent decline in ozone over Antarctica between January and April coincides with blooms of diatoms that appear to have low UV-B tolerance but are responsible for ~47% of annual primary production in Antarctic waters.
KEY WORDS: Antarctic · Marine protists · UV-A · UV-B · Ozone · Diatoms · Flagellates · Dinoflagellates
Resale or republication not permitted without written consent of the publisherAquat Microb Ecol 52: [131][132][133][134][135][136][137][138][139][140][141][142][143][144][145][146][147] 2008 due to the differing effectiveness of mechanisms to tolerate UV-B exposure, interspecific variation in UV-Binduced damage is reportedly high (e.g. Karentz et al. 1991). This has led to the suggestion that exposure to UV-B radiation may cause changes in the composition and abundance of marine protists with ramifications for trophodynamics and biogeochemical cycles (Laurion et al. 1998, Mostajir et al. 2000, Davidson & Belbin 2002, Sommaruga 2003.Remarkably few studies have addressed the effects of UV-B radiation on community-level interactions among marine microbes and fewer still have been performed in Antarctic waters (Davidson 2006). Some studies have shown that UV-B radiation has the potential to change the structure and function of Antarctic microbial communities (Smith et al. 1992, Davidson et al. 1996, Davidson & van der Heijden 2000, Davidson & Belbin 2002. However, as the results of community-level studies vary with environment, location and the composition of ...