Abstract

Interactions between climate change and UV radiation are having strong effects on aquatic ecosystems due to feedback between temperature, UV radiation, and greenhouse gas concentration. Higher air temperatures and incoming solar radiation are increasing the surface water temperatures of lakes and oceans, with many large lakes warming at twice the rate of regional air temperatures. Warmer oceans are changing habitats and the species composition of many marine ecosystems. For some, such as corals, the temperatures may become too high. Temperature differences between surface and deep waters are becoming greater. This increase in thermal stratification makes the surface layers shallower and leads to stronger barriers to upward mixing of nutrients necessary for photosynthesis. This also results in exposure to higher levels of UV radiation of surface-dwelling organisms. In polar and alpine regions decreases in the duration and amount of snow and ice cover on lakes and oceans are also increasing exposure to UV radiation. In contrast, in lakes and coastal oceans the concentration and colour of UV-absorbing dissolved organic matter (DOM) from terrestrial ecosystems is increasing with greater runoff from higher precipitation and more frequent extreme storms. DOM thus creates a refuge from UV radiation that can enable UV-sensitive species to become established. At the same time, decreased UV radiation in such surface waters reduces the capacity of solar UV radiation to inactivate viruses and other pathogens and parasites, and increases the difficulty and price of purifying drinking water for municipal supplies. Solar UV radiation breaks down the DOM, making it more available for microbial processing, resulting in the release of greenhouse gases into the atmosphere. In addition to screening solar irradiance, DOM, when sunlit in surface water, can lead to the formation of reactive oxygen species (ROS). Increases in carbon dioxide are in turn acidifying the oceans and inhibiting the ability of many marine organisms to form UV-absorbing exoskeletons. Many aquatic organisms use adaptive strategies to mitigate the effects of solar UV-B radiation (280-315 nm), including vertical migration, crust formation, synthesis of UV-absorbing substances, and enzymatic and non-enzymatic quenching of ROS. Whether or not genetic adaptation to changes in the abiotic factors plays a role in mitigating stress and damage has not been determined. This assessment addresses how our knowledge of the interactive effects of UV radiation and climate change factors on aquatic ecosystems has advanced in the past four years.

Highlights

  • Interactions between climate change, ozone, and ultraviolet (UV) radiation are altering exposure to UV radiation in aquatic ecosystems.[1,2] Climate change is causing the average global air temperature to rise and precipitation patterns to change, with important consequences for UV exposure in aquatic ecosystems

  • Judging from 30 years of field studies and satellite chlorophyll fluorescence data, cumulated densities of phytoplankton have decreased by 12% along the West side of the Antarctic Peninsula (Bellingshausen Sea), which has been attributed to increased solar UV-B radiation (280–315 nm) and rapid regional climate change.[13]

  • Understanding the role of interactive effects of dissolved organic matter (DOM), reactive oxygen species (ROS) concentrations, UV radiation and climate change in aquatic ecosystems will be important for sustaining structure and function of the aquatic ecosystem, for example, through fisheries production and the potential to use the water as a drinking water resource

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Summary

Introduction

Interactions between climate change, ozone, and ultraviolet (UV) radiation are altering exposure to UV radiation in aquatic ecosystems.[1,2] Climate change is causing the average global air temperature to rise and precipitation patterns to change, with important consequences for UV exposure in aquatic ecosystems. View Journal | View Issue ozone concentrations have decreased, but it is not clear if this trend will continue It is the first time the O3-depleted area is as large as that in the Antarctic.[11] Higher water temperatures resulting in a thinner mixing layer and longer growing season together with increased O3 depletion all have the potential to increase the exposure to UV radiation of aquatic organisms that live in the upper layers of the water column. Judging from 30 years of field studies and satellite chlorophyll fluorescence data, cumulated densities of phytoplankton have decreased by 12% along the West side of the Antarctic Peninsula (Bellingshausen Sea), which has been attributed to increased solar UV-B radiation (280–315 nm) and rapid regional climate change.[13] In the north of the Antarctic Peninsula, a lower photosynthetic biomass production is attributed to denser cloud cover and the resulting decreased PAR ( photosynthetic active radiation, 400–700 nm). In the past, capelin – an important prey for Atlantic cod – had a maximal distribution up to 75° N, but capelin were found up to 78° N in 2012 with cod following them.[24]

Increasing dissolved organic matter and exposure to UV radiation
Thermal stratification and exposure to UV radiation
Ocean acidification and exposure to UV radiation
Mechanisms of UV radiation damage
Parasites and pathogens
Bacteria and viruses
Interacting stress factors
Benthic organisms
Findings
Gaps in knowledge
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