2006
DOI: 10.1007/s00027-006-0819-4
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Inhibition of primary production by UV-B radiation in an arctic bay – model calculations

Abstract: Inhibition of primary production by UV-B radiation (UVBR) in Kings Bay, western Spitsbergen, was modelled using measured physical and biological data. The underwater radiation regime was modelled using continuous measurements of incoming radiation and repeated measurements of underwater attenuation of Photosynthetic Active Radiation (PAR) and UVBR. By using attenuation measurements, P/I curves and UVBR sensitivity measurements, we modelled the reduction of primary production in the photic zone for 14 days. We … Show more

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Cited by 15 publications
(10 citation statements)
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References 29 publications
(46 reference statements)
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“…In our case, the relationship between phytoplankton productivity and UVR sensitivity can be complicated by the addition of the acclimation processes (Banaszak 2003) or by a change in phytoplankton community structure that can occur during UVR stress (Sommaruga 2003). Changes in phytoplankton sensitivity towards UVR within small temporal or spatial scales has been shown earlier (Wängberg et al 2006 and references herein). Over the 3 days, we observed a good agreement between the changes in the UVR inhibition of the integrated PP measured with fixed and moving incubations.…”
Section: Discussionmentioning
confidence: 99%
“…In our case, the relationship between phytoplankton productivity and UVR sensitivity can be complicated by the addition of the acclimation processes (Banaszak 2003) or by a change in phytoplankton community structure that can occur during UVR stress (Sommaruga 2003). Changes in phytoplankton sensitivity towards UVR within small temporal or spatial scales has been shown earlier (Wängberg et al 2006 and references herein). Over the 3 days, we observed a good agreement between the changes in the UVR inhibition of the integrated PP measured with fixed and moving incubations.…”
Section: Discussionmentioning
confidence: 99%
“…Abiotic photoproduction of MeHg has been observed in the upper sunlit portions of some temperate lakes, in the presence of DOM (Siciliano et al 2005). Degradation of MeHg occurs through microbial action (Compeau and Bartha 1984;Oremland et al 1991) but can also occur through photochemical reaction (Constant et al 2007), which is induced primarily by UV radiation (Lalonde et al 2001;Wängberg et al 2006). MeHg has been detected in snow (Lahoutifard et al 2005;Constant et al 2007;Dommergue et al 2010), and up to 7.6% of the total Hg in an Arctic snowpack may be MeHg, based on one study area in the low Arctic tundra (Constant et al 2007).…”
Section: Methylmercury Photoreactivitymentioning
confidence: 97%
“…Methylmercury (MeHg, CH 3 Hg(I)), a toxic and bioaccumulative organic ion of Hg (Fitzgerald and Clarkson 1991), is also not simply a Hg reaction endpoint, with bioaccumulation a foregone conclusion. Rather, MeHg is a photoreactive species itself and also has the ability to be bound by particulates and organic matter, which will affect MeHg bioavailability (Sellers et al 2001;Wängberg et al 2006;Skyllberg et al 2006;Skyllberg 2008).…”
Section: Speciation Effects On Mercury Photoredox Reactions In Snowmentioning
confidence: 99%
“…Aquatic organisms that play important roles in carbon cycling such as phytoplankton, bacterioplankton, and coral reefs are damaged by UV radiation. The biological processes known to be affected by UV-B are primary production (Beardall and Raven, 2004;Leu et al, 2007;Wangberg et al, 2006), bacterioplankton growth (Hernµndez et al, 2007;Herndl et al, 1993;Jeffrey et al, 1996;Langenheder et al, 2006), and coral bleaching Anthony and Kerswell, 2007), enhancing the warming-related stress on corals Rodriguez-Roman et al, 2006). UV-B damages on algal photosynthesis include inhibitory effects on nutrient uptake and damage to DNA (Beardall and Raven, 2004 and refs.…”
Section: Introductionmentioning
confidence: 99%