TITLE: Overview of Marine Biotic Responses to Ozone Depletion AUTHOR: Raymond C. Smith DATE: 25-26 March 1996 PLACE: 1996 International Whaling Commission (IWC) Symposium on Climate Change and Cetaceans, Turtle Bay Hilton, Oahu, Hawaii [Talk might be abstract; is in ucmbo talks and ucmbo abs at the moment] Abstract It is now widely documented that reduced ozone will result in increased levels of ultraviolet (UV) radiation, especially UV-B (280-320nm), incident at the surface of the earth. There is considerable evidence that ultraviolet radiation (UV) can cause biological damage at the molecular, cellular, population and community levels and there is increasing evidence that these higher levels of UV-B radiation may be detrimental to various forms of marine life in the upper layers of the ocean. With respect to aquatic ecosystems, we also know that this biologically-damaging mid-ultraviolet radiation can penetrate to ecologically-significant depths in marine and freshwater systems. This knowledge, plus the dramatic decline in stratospheric ozone over the Antarctic continent each spring, now known to be caused by anthropogenically released chemicals, has resulted in a number of recent reviews and reports. In particular, the United Nations Environmental Program (UNEP) has provided recent updates (UNEP, 1989, 1991) with respect to the effects of ozone depletion on aquatic ecosystems and have concluded that "UV-B radiation in aquatic systems: 1) affects adaptive strategies (e.g., motility, orientation); 2) impairs important physiological functions (e.g., photosynthesis and enzymatic reactions); and 3) threatens marine organisms during their developmental stages (e.g., the young of finfish, shrimp larvae, crab larvae)". Possible consequences to aquatic systems include: reduced biomass production; changes in species composition and biodiversity; and alterations of aquatic ecosystems and biogeochemical cycles associated with the above changes. Consensus is building toward the view that current levels of UV play a major role as an ecological determinant, influencing both survival and distribution, and are thus deserving of increased study independent of ozone-related UV-B increases. On the other hand, there remains considerable controversy with respect to how laboratory and field results can be properly extrapolated to longer time and larger spatial scales and this problem is amplified by the exacting dosimetry required for quantitative results. At the ecosystem level there are few, if any, convincing data with respect to effects of ozone-related UV-B increases, there is considerable uncertainty, little consensus, and much work remains.