Microsoft Word - Rev-1-25-2392_s Engineering, Technology & Applied Science Research Vol. 8, No. 6, 2018, 3668-3672 3668 www. etasr. com Nazari-Sharabian et al: Climate Change and Eutrophication: A Short Review Climate Change and Eutrophication: A Short Review Abstract—Water resources are vital not only for human beings but essentially all ecosystems. Human health is at risk if clean drinking water becomes contaminated. Water is also essential for agriculture, manufacturing, energy production and other diverse uses. Therefore, a changing climate and its potential effects put more pressure on water resources. Climate change may cause increased water demand as a result of rising temperatures and evaporation while decreasing water availability. On the other hand, extreme events as a result of climate change can increase surface runoff and flooding, deteriorating water quality as well. One effect is water eutrophication, which occurs when high concentrations of nutrients, such as nitrogen and phosphorus, are present in the water. Nutrients come from different sources including agriculture, wastewater, stormwater, and fossil fuel combustion. Algal blooms can cause many problems, such as deoxygenation and water toxicity, ultimately disrupting normal ecosystem functioning. In this paper, we investigate the potential impacts of climatic factors affecting water eutrophication, how these factors are projected to change in the future, and what their projected potential impacts will be. Keywords-climate change; water quality; eutrophication I. INTRODUCTION The planet is getting warmer as an impact of exponentially increasing anthropogenic greenhouse gas emissions, especially CO2. According to the fifth assessment report of the Intergovernmental Panel on Climate Change (IPCC), the global average surface temperature has undergone a warming of 0.85°C (0.65 to 1.06) from 1880 to 2012, proving that global warming is occurring [1]. A warmer climate will affect the hydrological cycle and change atmospheric and meteorological properties such as precipitation patterns, atmospheric water vapor and evaporation [2-4], and consequently impact water quality by intensifying many forms of water pollution [5-7]. One form of water pollution is water eutrophication, which occurs when high concentrations of nutrients, such as nitrogen and phosphorus, are present in the water. In recent years, specific concerns about the impacts of climate change on water eutrophication, which causes global environmental challenges regarding the management of water resources, have been raised [8-15]. The Fifth Global Environment Outlook (GEO-5) reports that more than 40% of water bodies all around the world suffer from different levels of eutrophication [16]. The reason for this phenomenon is an important issue of great concern is its potential consequences, threatening the reliable supply of drinking water [17-19]. The terminology and application of trophic development of freshwaters date back to the early twentieth century. The consequences of anthropogenic-induced eutrophication of freshwaters did not become evident until the 1940s and 1950s as public concern over the severity of surface water deterioration became evident and triggered expanding scientific interest. Scientists debated which nutrient is primarily responsible for limiting productivity in lakes and rivers, an issue known as limiting nutrient controversy, and they ultimately agreed that phosphorus (P) is the key element in controlling eutrophication. [20]. Algal blooms in water bodies are a sign of eutrophication that indicates the presence of high concentrations of phosphorus and nitrogen. Algal blooms can form anoxic environments in the water and consequently deteriorate water quality [10, 15, 21]. Predictions indicate that with rising concentrations of atmospheric CO2, the occurrence of algae blooms will likely increase [22, 23]. Recent anthropogenic changes, such as urban, agricultural, and industrial development, have accelerated the progress of nutrient over-enrichment, leading to eutrophication in water bodies [24-26]. Undesirable symptoms of eutrophication primarily occur during the plant growing season (spring and summer), when low flow, high water residence times, sufficient light levels and high water temperature promote rapid algal growth. During the growing season, the eutrophication risk mainly originates from point discharges, a major source of high concentrations of dissolved, bioavailable phosphorus fractions. At times when diffuse agricultural runoff contributions are relatively low, phosphorus concentrations from point sources become even higher in the receiving water bodies, as a result of reduced effluent dilution [27]. The trophic state in flowing waters depends mainly on phosphorus and nitrogen levels. Hydraulic flushing of nutrients, light limitation, and water velocity are essential in controlling algal growth. This suggests that rivers or riverine lakes with short retention times (<3 days) will show different effects compared to those with long retention times (>3 days) [28]. Climate change can, directly and indirectly, affect eutrophication, as a result of interactions between meteorological factors and nutrient availability [24, 29]. The Mohammad Nazari-Sharabian Department of Civil and Environmental Engineering and Construction, University of Nevada, Las Vegas, Las Vegas, USA nazarish@unlv. nevada. edu Sajjad Ahmad Department of Civil and Environmental Engineering and Construction, University of Nevada Las Vegas, Las Vegas, USA sajjad. ahmad@unlv. edu Moses Karakouzian Department of Civil and Environmental Engineering and Construction, University of Nevada Las Vegas, Las Vegas, USA mkar@unlv. nevada. edu Engineering, Technology & Applied Science Research Vol. 8, No. 6, 2018, 3668-3672 3669 www. etasr. com Nazari-Sharabian et al: Climate Change and Eutrophication: A Short Review existing literature shows that sensitive factors to climate change such as water temperature, precipitation, wind, and solar radiation can affect trophic conditions in water bodies. Therefore, to maintain water resources availability and safety, it is crucial to investigate the impacts of climate change on water quality in water resources. This paper briefly summarizes the potential impacts of climate change on the occurrence of eutrophication in water resources. II. CLIMATE CHANGE EFFECTS A. Temperature Regarding climate change, many factors are considered in order to predict how future global warming will occur. In this case, the amount of future greenhouse gas emissions is a key variable. Two different emissions scenarios, including RCP2.6 (low emissions scenario) and RCP8.5 (high emissions scenario), show that by the end of the 21st century, the global surface temperature is expected to increase by 0.3°C-1.7°C and 2.6°C-4.8°C under RCP2.6, and RCP8.5, respectively [30]. Temperature is an important environmental factor that influences chemical and physical properties in water ecosystems such as pH, salinity, solubility, and diffusion rates, and can consequently affect water eutrophication potential [31, 32]. Air temperature and temperature in water bodies are in close equilibrium. Hence one of the immediate reactions to climate change is expected to be alterations in river and lake water temperatures [22, 33-35]. When water temperature and nutrient concentrations increase, algae growth is stimulated, leading to water eutrophication and algal blooms. As concentrations of phosphorous and nitrogen increase in lakes, rivers and estuaries, cyanobacteria become increasingly dominant. Cyanobacteria are a group of bacteria that grow in any type of water (fresh, brackish, or marine) and use sunlight to create food and survive. Because of their color, they are commonly known as “blue-green algae”. They grow quickly and bloom in warm, nutrient-rich environments. Water bodies experiencing frequent blooms of cyanobacteria show properties that can impact water quality as well as the health of the surrounding environment [36, 37]. Once the water temperature rises above 25°C, the growth of cyanobacteria accelerates [32, 38-40]. Similarly, warmer temperatures could also stimulate earlier and more extended periods of potential algal blooms, as the immediate direct effect of a warmer environment [31, 41, 42]. Moreover, warmer temperatures will affect nutrient loadings from soil and sediment, which can ultimately impact the trophic status of water [43]. As the inflow to a reservoir gets warmer as a result of higher temperature, the water column will stratify more intensely, decreasing nutrient availability in the surface water. In this case, cyanobacteria will obtain nutrients from deeper depths and accelerate nutrient release in water [44, 45]. Higher temperatures will accelerate microbial activity in sediments at the bottom of lakes and rivers. In this case, the release rate of internal phosphorus will increase, and will contribute to a significant portion of the total nutrient load in the water [46]. In addition, higher water temperatures will reduce the degradation coefficients of water and decrease its self-purification capacity [10]. Therefore, under climate change conditions, the release of nutrient loadings from internal sources could still make water eutrophic, even if external sources of nutrients, such as waste discharge and non-point pollution are restrained [47]. Moreover, when the surface water gets warmer, water viscosity will decrease, and as a result, nutrient diffusion will increase towards the surface. In this situation, larger phytoplankton (photosynthesizing microscopic biotic organisms that inhabit the upper sunlit layer of almost all oceans and bodies of fresh water on Earth) will sink, and cyanobacteria will become more abundant [38, 48, 49]. As a summary, increasing air temperature will increase water temperature and deteriorate water quality conditions by accelerating the eutrophication process in water bodies, which can cause environmental and health-related issues [23, 26, 46]. B. Precipitation Besides the temperature effects, the change in hydrological regimes is also a consequence of climate change. As the temperature is predicted to rise, precipitation will not change uniformly [30]. Under the RCP2.6 and RCP8.5 scenarios, climate model mean projections for 2081-2100 compared to 1986-2005 indicate that annual mean precipitation will increase mostly around the equatorial Pacific and some high-latitude areas. However, projections show that mean precipitation is likely to decrease in certain mid-latitude and subtropical regions, although some increase in mean precipitation in many mid-latitude regions is also likely to occur under the same scenario. Therefore, in areas with projected higher precipitation, it is possible that intense extreme precipitation events will occur and cause more erosion and resuspension of sediments, ultimately resulting in higher concentrations of sediments and nutrients in receiving water bodies [24, 48]. Furthermore, these extreme events will increase contaminant discharge and affect non-point pollution by mobilizing them over land and increasing nutrient concentrations in receiving water bodies, consequently degrading water quality. [49, 51- 53]. Less precipitation can also increase the risk of eutrophication by lowering minimum flows. In this case, less water volume will be available for dilution of pollutants. As a result, increased concentration of contaminants can cause deoxygenation, by lowering dissolved oxygen concentration (DO) and increasing biochemical oxygen demand (BOD). Consequently, the risk of eutrophication, especially in water bodies with limited re-aeration capacity, will be increased [24, 54]. Therefore, under climate change conditions and due to the alteration of regional precipitation patterns, water bodies are exposed to greater nutrient loads, which can ultimately lead to water quality deterioration. C. Wind The wind will also be affected by climate change, and will have direct and indirect impacts on water resources [39]. Authors in [50] used general circulation models, under the A2 emission scenario, to predict the wind speed in different regions in 2050. Modeling results showed that across the boreal regions of the northern hemisphere, including Canada, tropical and subtropical regions, northern Europe, and Central and South America, stronger surface wind speeds will occur in 2050, while decreasing wind speeds were predicted for southern Europe, East and South Asia, and much of the west coast of South America. The direct effects of wind refer to Engineering, Technology & Applied Science Research Vol. 8, No. 6, 2018, 3668-3672 3670 www. etasr. com Nazari-Sharabian et al: Climate Change and Eutrophication: A Short Review blowing of algae from the water surface to the lakeshore or river banks and influencing these regions by forming algal blooms and changing environmental conditions. The indirect effect is the disturbance caused by the wind, which can circulate the water and mix different layers of the water column. This circulation enhances the mixture of nutrients and accelerates the release of nutrients from sediments [55]. Also, as the air temperature rises, wind mixes the warmer upper layers of water with the colder lower layers, which can speed up the volatilization, migration, and transformation of pollutants [9]. Authors in [56] used different sediment resuspension models to simulate nutrient distributions in the wind-dominated Salton Sea in the United States, which is highly eutrophic. They concluded that sediment resuspension, which induces both particulate and dissolved forms of nutrients, is the critical factor in nutrient cycling of the sea. Therefore, higher wind speeds will accelerate sediment resuspension, contaminant circulation, and finally exacerbate trophic conditions. Moreover, authors in [57] studied the Taihu Lake in China, which has experienced periods of severe eutrophication in the past. Model results, which coupled the biological processes and hydrodynamics in the lake, showed that temporal variations of eutrophication have high dependencies on meteorological forces. On the other hand, intense and high-speed winds can also restrain the formation of algal blooms by dissipating them and weakening their aggregation [58]. Therefore, the wind will have direct and indirect impacts on water trophic conditions, but it does not act as a single decisive operator, and mostly influences eutrophication along with other meteorological factors. D. Solar Radiation Global warming and solar radiation have mutual connections [59]. As an important source of energy, solar radiation plays a crucial role in photosynthesis in different ecosystems and is an essential factor for the growth of phytoplankton and other aquatic species. Therefore, the photosynthesis efficiency is dependent upon the temporal and spatial variations of solar radiation. Sufficient sunlight increases water temperature and the presence of nutrients altogether provide suitable conditions for the growth of algae and phytoplankton, finally resulting in water eutrophication [22]. Solar radiation affects a wide range of living organisms, by penetrating aquatic systems and acting as the energy source for plant photosynthesis. If plants do not receive sufficient amounts of sunlight, they take up oxygen from the water, and DO depletion will occur. Under anaerobic conditions, phosphorus release from sediments can cause water eutrophication [60, 61]. Algae distribution is also dependent on the intensity of solar radiation received at different depths. However, increased sunlight will not necessarily cause more algae growth. There is a maximum growth rate for algae, in which beyond this threshold, the growth rate will decrease [62, 63]. Authors in [62] projected UV-B radiation at the Earth’s surface from 1960 to 2100. Although the global temperature is slated to rise until 2100, results of UV-B predictions showed that radiation change at different latitudes will alter differently. Projected UV-B radiation compared with 1980 levels, showed increasing trends at 60˝ to 90˝ southern latitude (more than 20% increase), and decreasing trends at 60˝ to 90˝ northern latitude (around 10% decrease). E. Summary Besides the effects of temperature, precipitation, wind and solar radiation alteration, an increasing population, rapid urban development, and lack of land use planning continually contribute to the degradation of the environment and water resources. Figure 1 summarizes the impacts of climate change on water eutrophication. Climate Change Factors Air Temperature Precipitation Wind Speed Solar Radiation Human Activities Direct Effects Indirect Effects Water Temperature, pH, Solubility, Viscosity Growth and Reproduction of Algae Accumulation of Phytoplankton Ecosystem Degredation Self-purification Capacity Microbial Activities Water Viscosity and Nutrient Diffusion Stratification Release and Transport of Internal Nutrients Change of Hydrological regimes Uneven Distribution of Water resources Water Cycle Water Level Water Quality Runoff Degradation Coefficients Extreme Events, Droughts, Flood, etc. Water Pollution Water Quality Degredation Nutrient Release Water Stability Aggregation of Algae Mixing of Nutrients Formation of Blooms Migration of Pollutants Photosynthesis Sunlight Degradation and Intensity Transparency Light Respiration Phototoxicity Dissolved Oxygen Algae Growth Pollution Discharges External Nutrient Loads Eutrophication Fig. 1. The interaction among climate change factors and eutrophication. Engineering, Technology & Applied Science Research Vol. 8, No. 6, 2018, 3668-3672 3671 www. etasr. com Nazari-Sharabian et al: Climate Change and Eutrophication: A Short Review III. CONCLUSION In this paper the effects of climate change on meteorological parameters such as temperature, precipitation, wind, and solar radiation were reviewed, and their potential impacts on water quality, especially eutrophication, were investigated. Based on the available literature and historical, scientific evidence, a changing climate will lead to degradation of water quality. The recent anthropogenic climate change will also amplify deterioration of trophic conditions in water resources, by changing the internal and external nutrient loadings, as an impact of global temperature rise, changing precipitation patterns, and altering wind speed and solar radiation intensity. 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