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Climate Change Impacts on Energy in the Great Lakes Basin KEY MESSAGE: Climate change is predicted to have negative impacts on the energy sector in the Great Lakes Basin. Warmer water temperatures, lower lake levels, and a greater frequency of intense storm events may result in less-efficient power plants and damaged energy infrastructure. Decision makers should address these impacts with policies that increase power plant efficiency, increase infrastructure resilience, lower overall energy demand, and prevent water diversions from the basin. T he Laurentian Great Lakes, comprised of Lakes Huron, Erie, Michigan, Ontario, and Superior, are home to more than 35 million people in the United States and Canada (USEPA 2012). With an overall volume of 5,439 mi3 (22,684 km3), the Great Lakes are the world’s largest source of surface freshwater, containing 21 percent of the global supply (GLERL 2014). The Great Lakes Basin lies within eight U.S. states and two Canadian provinces and includes the lakes, connecting channels, tributaries, and groundwater that drain through the international section of the St. Lawrence River, combining for a total surface area of over 94,000 mi2 (243,000 km2) (USEPA 2012). Water and Energy in the Great Lakes Basin Figure 1. Daily water withdrawal rates for the energy sector in U.S. Great Lakes states. Source: Mills & Sharpe 2010. The Great Lakes Basin produces a large amount of energy. In 2011, the basin contained 583 powergenerating facilities capable of producing nearly 670,000 MW of electricity, which is enough energy to power about 45 million homes (GLC 2011). Most of that power comes from coal-fired power plants, which produce 39.4 percent of the basin’s electricity. Natural gas, nuclear power, and hydropower produce 28.9, 16, and 9.1 percent of the region’s power, respectively. The average power plant in the Great Lakes Basin is 41 years old, with ages ranging from 1-109 years old. This level of energy production requires vast amounts of water (Figures 1 & 2). Coal-powered thermoelectric plants are the largest water users, withdrawing 15,924 million gallons (60,278 megaliters) per day and consuming 160 million gallons (606 megaliters) per day (GLC 2011). Nuclear power plants are the next largest users, withdrawing 7,638 million gallons (28,912 megaliters) per day and consuming 227 million gallons (859 megaliters) per day. Plants generating power from natural gas, oil, and renewable sources withdraw another combined 1,435 million gallons (5,432 megaliters) per day from the basin. Overall, the energy sector in the Great Lakes Basin is highly reliant on the system’s freshwater resources. Climate Change Impacts on Energy Climate change is predicted to have a variety of effects on water resources in the Great Lakes Basin. General circulation models (GCMs) using future CO2 scenarios predict changes in several climate parameters that will affect water quality and quantity (Figure 3). By 2090, air temperature is predicted to increase 1.8-12.6° F (1-7° C), which will drive warmer water temperatures (Lofgren et al. 2002, Gregg et al. 2012). Evaporation rates are expected to increase 16-39 percent by 2090 (Lofgren et al. 2002), due largely to an annual winter ice cover that has decreased by 71 percent since 1973 (Gregg et al. 2012). Higher evaporation rates will likely drive down lake levels, with some models estimating a decrease of as much as 8.2 feet (2.5 meters) by 2090 (Lofgren et al. 2002). Climate change will also alter weather patterns in the Great Lakes Basin. Occurrences of extreme weather events, such as intense storms and prolonged droughts, are expected to increase, but predict- ed trends in overall preand shoreline erosion. cipitation are more amAn aging system of biguous, with GCM pretransmission lines will dictions ranging from a not be able to withstand 20 percent increase to a more intense storm acnine percent decrease tivity. Wind turbines (Lofgren et al. 2002). may experience wind Several of these cli- Figure 2. Daily water withdrawal rates, in millions of gallons per conditions outside of mate change effects will their safe operating limday, of thermoelectric power plants in the Great Lakes Basin. have negative impacts its. Overall, existing enSource: GLC 2011. on the energy sector. ergy infrastructure will First, warmer intake water will reduce the cooling effihave to adapt to maintain current capacity in coming decciency of thermopower plants, thus inhibiting their caades under such intense weather conditions. pacity to generate power safely. In July 2006, the Cook While warmer water temperatures and lower lake Nuclear Plant in Michigan was shut down due to highlevels are expected to decrease the efficiency of power temperature intake waters caused by an intense heat plants, the extent of these decreases is unknown. Uncerwave (Krier 2012). Conditions inside the containment tainty regarding the magnitude and interactions of clibuilding became too warm to accomplish daily tasks and mate change effects make reliable estimates of their imthe plant remained closed for five days until air and wapact on energy supplies challenging. In addition, a growter temperatures decreased to viable levels. Warmer ining population in the Great Lakes Basin will increase the take water also leads to warmer discharge water, which demand for energy, adding further stress to the basin’s can pose a threat to the surrounding environment. Power capacity. plants will increasingly find themselves in noncompliance with heat discharge permits issued by state authori- Policies Moving Forward ties. Already, there have been a handful of cases where the Illinois Environmental Protection Agency has had to Great Lakes policymakers must focus on several key make exceptions and allow power plants to discharge areas in order to address the impacts of climate change water at higher temperatures than their permits allow due on the energy sector. The first is to promote waterto the increased temperature of the incoming water efficient power plant technology. The majority of exist(Meyer & Wernau 2012). ing thermoelectric power plants use an open-cycle coolLower lake levels and prolonged periods of drought ing system that requires the withdrawal of large amounts will also reduce the quantity of water available for ener- of water. Power plants equipped with an alternative gy production. In the case of thermopower plants, inade- closed-cycle cooling system withdraw 97-99 percent less quate intake water means a reduction in cooling efficien- water while still producing comparable amounts of enercy and a subsequent reduction in power generation cagy (GLC 2011). Adopting such technology would vastly pacity. For hydropower plants, inadequate intake water reduce the amount of intake water needed for cooling directly reduces power generation. Michigan’s Cloverand the amount of high-temperature water discharged land Electric Cooperative experienced a 60-80 percent into the environment. decrease in energy output from its Sault Sainte Marie Another way policymakers can blunt the impact of hydropower plant in 2012 (Kowalski 2013). The plant climate change is by increasing the resilience of energy withdraws its water from a canal near Ashmum Bay, infrastructure throughout the basin. A higher frequency which, like the rest of Lake Superior, was experiencing of intense storms will likely cause extensive damage to record-low water levels. A temporary fix that involved the existing facilities and equipment that produce and lowering 2,000 concrete blocks into the bay to raise watransmit electricity. Policymakers should concentrate ter levels cost the utility approximately $300,000. efforts on reinforcing coastal energy facilities, hardening Finally, an increase in intense storm events in the transmission lines, and expanding the safe operating limGreat Lakes Basin could potentially damage energy inits of energy production equipment, such as wind turfrastructure, thereby decreasing energy capacity. Coastal bines. power plants are susceptible to increased wave action Furthermore, policymakers can reduce the impact of climate change by reducand strengthen the Coming overall energy depact’s restrictions to mand in the basin. Policy avoid direct humanthat promotes industrial, caused decreases in lake municipal, and individulevels. al energy conservation In conclusion, enerand efficiency would gy and water in the greatly reduce the growGreat Lakes Basin have ing strain on energy caan interdependent relapacity in the basin. tionship that may be While programs addressnegatively impacted by ing this issue exist in climate change. In the Figure 3. GCM predictions for Lake Michigan-Huron climate many Great Lakes states change effects. Source: Lofgren et al. 2002. coming decades, predictand provinces, increasing ed increased water temdemand from a growing population requires a redoubling peratures, lower lake levels, and a higher frequency of of efforts to meet the future energy needs of the basin. intense weather events will lower power plant efficiency Finally, policymakers must limit the amount of water and damage existing energy infrastructure. Policymakers withdrawn from the basin in order to maintain lake levmust address these challenges by promoting initiatives els. The Great Lakes Compact, signed in 2008 and is a and regulations that increase power plant efficiency, inbinding interstate compact between the eight U.S. Great crease infrastructure resilience, decrease overall energy Lakes states, prohibits the withdrawal of water by cities demand, and decrease water diversions from the basin. and counties outside of the Great Lakes Basin (WDNR 2013). While this prohibition is currently helping to - Authored by Victoria Lubner; Edited by Will Kort & maintain lake levels, future challenges to the Compact Aaron Thiel; Supervised by Dr. Jenny Kehl may ease withdrawal restrictions, allowing diversions to carry water out of the basin. Policymakers must uphold References Egan, D. 2013, July 27. Does Lake Michigan’s record low mark beginning of new era for Great Lakes? Milwaukee Journal-Sentinel. Retrieved from http://www.jsonline.com/news/wisconsin/does-lake-michigans-record-low-water-level-mark-beginning-of-newera-for-great-lakes-216429601.html Gregg, R., K. Feifel, J. Kershner, & J. Hitt. 2012. The state of climate change adaptation in the Great Lakes region. General report. Bainbridge Island, WA: EcoAdapt. Great Lakes Commission (GLC). 2011. Integrating energy and water resources decision making in the Great Lakes basin. Report of the Great Lakes Energy-Water Nexus Team. Ann Arbor, MI: Author. Great Lakes Environmental Research Laboratory. 2014. About our Great Lakes: Economy. Retrieved from http://www.glerl.noaa.gov/ pr/ourlakes/economy.html Kowalski, K. 2013, July 16. Low Great Lakes levels raise concerns for Midwest power plants. Midwest Energy News. Retrieved from http://www.midwestenergynews.com/2013/07/16/low-lake-levels-raise-concerns-for-midwest-power-plants/ Krier, R. 2012, August 15. Extreme heat, drought show vulnerability of nuclear power plants. Inside Climate News. Retrieved from http://insideclimatenews.org/news/20120815/nuclear-power-plants-energy-nrc-drought-weather-heat-water Lofgren, B., Quinn, F., Clites, A., Assel, R., Eberhardt, A., & Luukkonen, C. (2002). Evaluation of potential impacts on great lakes water resources based on climate scenarios on two GCMs. Journal of Great Lakes Research, 28(4), 537-554. Meyer, K. & J. Wernau. 2012, August 20. Power plants releasing hotter water. Chicago Tribune. Retrieved from: http:// articles.chicagotribune.com/2012-08-20/news/ct-met-nuclear-water-20120820_1_power-plants-midwest-generation-plantoperators Mills. P.C. & J.B. Sharpe. 2010. Estimated withdrawals and other elements of water use in the Great Lakes basin of the United States in 2005. Scientific investigations report 2010-5031. Reston, VA: U.S. Geological Survey. United States Environmental Protection Agency (USEPA). 2013. Basic Information. Retrieved from http://www.epa.gov/greatlakes/ basicinfo.html Wisconsin Department of Natural Resources. (WDNR) 2013. The Great Lakes compact. Retrieved 2014, January 21 from http:// dnr.wi.gov/topic/greatlakes/compact.html