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2_23 A dltliirial <br />The general effects of climate change on freshwater <br />systems will likely include increased water tempera- <br />tures, decreased dissolved oxygen levels, and increased <br />toxicity of pollutants thereby altering the availability <br />and quality of habitat for aquatic biota (reviews in <br />Mulholland et al. 1997, Allan et al. 2005, Ficke et al. <br />2007). Meyer et al. (1999) identified characteristics <br />of aquatic ecosystems that are particularly sensitive <br />to climate change (Table 2 -5). These highlight the <br />range of impacts climate change poses to the biota of <br />freshwater systems — ranging from loss of habitat and <br />the resulting shifts in species composition to changes <br />in nutrient cycling that affect oxygen and nutrient <br />availability —and the indirect effects of synergies with <br />other stressors. <br />Changes in global climate affect primary produc- <br />tion and the nutrient concentration of inland waters <br />(reviewed in Ficke et al. 2007). Increased produc- <br />tivity resulting from warmer temperatures can lead <br />to oxygen depletion in bottom waters as algae and <br />organic matter settle out of surface waters and <br />decompose. Water quality is also likely to be influ- <br />enced by climate - induced changes, with potential <br />consequences for aquatic organisms (reviewed in <br />Murdoch et al. 2000). Warming of surface waters <br />and longer growing seasons have the potential to <br />increase primary production, organic matter decom- <br />position, and nutrient cycling (Mulholland et al. <br />1997), particularly in systems with sufficient nutri- <br />ent and oxygen supplies. Productivity will be affect- <br />ed by changes in the hydrologic cycle that impact <br />nutrient loading and residence times. For example, <br />more frequent storm events may flush nutrients and <br />sediment into surface waters. In addition, warmer <br />water temperatures may increase productivity as <br />a result of increased metabolic rates. During drier <br />climatic periods, decreased stream flow may increase <br />the residence time and concentrations of nutrients <br />and pollutants in surface waters. However, in oxygen <br />poor systems, decreased oxygen holding capac- <br />ity associated with warmer water temperatures may <br />actually exacerbate low oxygen availability and limit <br />productivity. <br />Table 2 -5. Some properties of aquatic ecosystems that are particularly sensitive to climate change <br />(Source: Meyer et al. 2002, © Wiley Interscience, used with permission). <br />Lakes <br />Streams <br />Wetlands <br />Mixing Regime <br />Flow Regime <br />Altered Water Balance Leading to <br />Wetland Losses <br />Nutrient and DOC Inputs <br />Sediment Transport/ Channel <br />Fire Frequency <br />Alterations <br />Habitats Meeting Temperature and <br />Nutrient Loading and Rates of <br />Altered Rates of Exchanges of <br />Oxygen Requirements <br />Nutrient Cycling <br />Greenhouse Gases <br />Productivity <br />Fragmentation and Isolation of Cold <br />Vegetation Species Composition <br />Water Habitats <br />Top Predator Changes Leading to <br />Altered Rxchanges with the Riparian <br />Reproductive Success of Many <br />Trophic Cascades <br />Zone <br />Animal Species <br />Abundance of Cold- and Warm- <br />Life History Characteristics of Many <br />Sensitivity to Invasion by Tropical <br />Water Fish Species <br />Aquatic Insects <br />Exotic Species <br />