Efficient usage of waste heat by applying a seasonal energy storage (BTES) at ITT Water & Wastewater AB, Emmaboda, Sweden

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Efficient usage of waste heat by applying a seasonal energy storage (BTES) at ITT Water & Wastewater AB, Emmaboda, Sweden ( efficient-usage-waste-heat-by-applying-seasonal-energy-stora )

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net savings will be 1 950 Thousand SEK. This indicates a straight pay back time of 4 years (grants included) or 5, 5 years (grants excluded). 8. ENVIRONMENT AL ISSUES The environmental evaluation is based on the following technical properties of the system: • The heat carrier between the BTES and the local district heating consists of water in closed loop that has no physical contact to other flowing media in system except the ground water in the bedrock. • The water will have no additives and will consist of local tap water. • The flow will be regulated by one or several frequency controlled circulation pumps. The pressure will be low, approx. 2 bar as a maximum. • The rock around the boreholes will be heated up to maximum +70oC. The highest temperatures will occur close to each one of the boreholes. The highest average temperature of rock mass will be +60oC fully charged, and +40oC as lowest when fully discharged. During construction a temporary lowering of the ground water in the rock is expected. However, the rock has a low permeability and the disturbance will therefore be limited to a narrow area. The tap water used as heat carrier is oxidized and may to some extent mix with a slightly reduced ground water that occurs in fractured part of the rock. If so, iron and manganese in solution may precipitate in the fissures and clog these. However, the amount of precipitates is estimated to be very low, but on a very long term, the permeability of the rock may be locally decreased. The type of borehole heat exchanger used will allow hot water to have direct contact with the borehole walls. In theory, some of the minerals would get into solution in the water. However, results from IEA research on this subject clearly indicate that the risk for such processes is very low with actual types of rocks and temperatures (Snijders 1995). The IEA research also shows that an increase of temperature up to +70oC will kill all bacteria in the centre of the storage. Along the sides with temperatures of +45oC and less, the micro fauna will adopt with new species of mainly iron-, sulphur-, methane-, and nitrogen bacteria. However, an increased temperature will not lead to an increased growth of bacteria since growth is mainly controlled by an increased access to nutrients, such as organic coal. It shall also be considered that the natural bacteria fauna will be return back to normal once the storage is shut down and the rock is slowly recovered to ambient temperature. Heat that is stored in the rock mass can be transported away with the flow of ground water. The two investigation holes suggest that there are a couple of fracture zones that in theory may displace some of the heat being stored. However, based on the fact that the ground water gradient is very small (approx. 1/100), and that the hydraulic conductivity of the bedrock is low (10-6 m/s), no spreading of heat is expected. (In theory the flow of ground water is less than 0, 5 m/year). The calculated losses from the storage is 1 200 MWh annually. This heat will mainly reach the surface at storage area, approx. 5 000 m2. Theoretically estimated the heat losses at surface will be in the order of 30 W/m2. This is about 500 times more than the natural heat flux from the

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