Del 2.3 Technology specification for different E-HUB district scenarios

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Contract Number 26165 E-HUB Energy-Hub for residential and commercial districts and transport SEVENTH FRAMEWORK PROGRAMME Grant Agreement No: NMP2-SL-21-26165 Call identifier: FP7-21-NMP-ENV-ENERGY-ICT-EeB Del 2.3 Technology specification for different E-HUB district scenarios Due date of deliverable: 15/3/212 Actual submission date: 18/5/212 Start date of project: 15/12/21 Duration: 48 months Organisation name of lead contractor for this deliverable: SOLINTEL Author(s): David Lanceta Alonso (SOLINTEL) Adrián Aguilar Villamor (SOLINTEL) Sattaya Narmsara (FRAUNHOFER-ISE) Florian Kagerer (FRAUNHOFER-ISE) Jan Kuhlman (HSW) Björn Oldorf (HSW) Dries Vos (VITO) Johan van Bael (VITO) Johan Desmedt (VITO) Hans van Wolferen (TNO) Frans Koene (TNO) Giorgio Urbano (D APPOLONIA) Alberto Traverso (TPG-DIMSET) Leonardo Subías Subías (ACCIONA) Paola Laiolo (ISPE) Dissemination Level: Public (PU) Revision: final

1 Executive Summary The E-Hub project, funded under the FP7 programme Energy efficient Buildings (EeB) aims at developing energy infrastructure concepts that are able to utilise the full potential of renewable energies available at district level. An important element of such concepts involves smart control of energy producers 1 and consumers in a district. An important question is what kind of energy producing and consuming equipment is suitable for use in smart energy networks. The selection of suitable energy generation and distribution systems is the objective of the present study ( define possible district scenarios ). The optimisation process and the comparison with a conventional system, using the system impact calculation model, will be the subject of Deliverable 2.4 E-Hub system impact calculation model. As the starting point serve the 6 model districts identified in Deliverable 1.1 Identification and systematic specification of a model district type. These model districts are summarized in the table below. The table shows that in fact 4 different districts have been identified and that district no. 2 is located in three different climate zones in order to take the effect of the climate into account. Model district type Description climate zone District could be located in: MDT1 Urban or suburban, mixed use (i.e. residential, commercial and services), medium density mid-rise buildings from 1946 to present MDT2A Residential district, suburban or exurban area, buildings aged from 1971 to present, medium/low density, mid-rise buildings (South Athens Palermo Malaga MDT2B Residential district, as 2A (North Helsinki MDT2C Residential district, as 2A Tweewaters MDT3 Business district/office park in a metropolitan or urban area with medium density high-rise and mid-rise buildings aged from 1981 to present MDT4 Multifunctional development centre with mixed use (i.e. residential, commercial and services), with medium density mid-rise buildings aged from 1981 to present Table 1: Table showing 4 different model districts, of which district no. 2 is located in 3 different climates The size of the model districts, with a few hundred inhabitants, is not as large as a real district which typically has 5-1 inhabitants. However, the model districts are treated as a typical module of which a district can contain several. The size of the model district, illustrated in the next figure, is taken to size the energy system (e.g. central boiler or district heating network). 1 Strictly speaking, energy cannot be produced (nor annihilated). Energy is used here as a generic term for forms of energy such as heat, cold and electricity which can be converted from e.g. fossil fuels or solar energy.

kwh Figure 1: 3D model of model district MDT1 with district heating network and district heating station shown in red. The districts considered contain buildings in the current state of thermal insulation because the impact of applying E-hub systems on (far more abundant) existing districts is much larger than when considering new and more energy efficient districts. In the present study the energy demand of the model districts was analysed in detail, in particular producing hourly data for the energy consumption using the equest software from the DOE (Department of energy) (See Annex A). However, assessment of the energy consumption was done mainly on the basis of the monthly energy profiles, as illustrated in the figure below for model district no. 1 (). This is the subject of chapter 3. 4 District energy demand - MDT1-35 3 25 2 15 1 Heating DHW Cooling Electricity 5 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Figure 2: Figure showing the monthly energy demand for heating, DHW, cooling, and electricity in kwh/month for model district no.1 (). Electricity consumption includes the energy for building ventilation, lighting and auxiliary equipment In the next step, a number of real cases were studied which provided information on the performance and economic feasibility of different renewable energy and energy efficient systems. The cases studied are summarized in the table below. Detailed information can be found in Annex B.

Technology Photo Voltaic panels Windturbines Solar collectors Real case study Electricity production with 1.8 kwp poly-crystalline photovoltaic modules in Belgium. Electricity production with a 2.4 kwp poly-crystalline photovoltaic module in Belgium. Electricity production with a 1.2 kwp poly-crystalline photovoltaic module in Belgium. Electricity production with a 66 kw wind turbine in Middelkerke, Belgium. Electricity production with a 1,65 kw wind turbine in Halle (Belgium). Electricity production with a 1,8 kw wind turbine in Eeklo (Belgium). Domestic hot water production with 37 m² of solar collectors combined with space heating with gas boilers Domestic hot water production with 51 m² vacuum tube solar thermal collector for an elderly home in Schoten, Belgium. Domestic hot water production with a 33 m² flat plate solar thermal collector for an elderly home in Mol with 28 apartments (Belgium). Domestic hot water production with a 82 m² flat plate solar thermal collector for an elderly home in Kortrijk, Belgium. CHP (Combined heat Heat production with a 1 kw wood pellet boiler in combination with a 2 kw and Power) condensing gas boiler for space heating of 26 dwellings in Belgium. Absorption cooling district heating Heat pump ORC-CHP (Organic Rankine Cycle Combined Heat and Power) in a residential district (38 dwellings) Heat and electricity production with a 5,5 kwe/12.5 kwth Combined Heat and Power installation (CHP) for the energy supply of 12 dwellings in Herenthout (Belgium). Micro-CHP in a residential building (94 dwellings) in Madrid Cogeneration plant in Genoa (Sampierdarena neighbourhood) Absorption cooling with a cooling capacity of 3,2 kwth at the AZ Sint-Jan Hospital in Bruges, Belgium. District heating of public buildings and private dwellings fuelled by local biomass in Liguria region (Italy) Heat production with a 1.5 kwth direct expansion heat pump. Underground heat and Borehole heat exchanger field for the art museum in Ahrenshoop (Germany) cold storage Hydrogen storage Energy piles for an office building in Schwerin (Germany) Heat and cold production with two heat pumps of 195 kwth and an aquifer thermal energy storage system (ATES) for a hospital. Aquifer thermal energy storage to provide heat and cold at Cipal and Technologiehuis in Geel, Belgium. Aquifer thermal energy storage to provide heat and cold with a nominal power of 518 kwth at the site of NV Blairon in Turnhout, Belgium. Aquifer thermal energy storage to provide heat and cold with a nominal power of 57 kwth at Etap in Malle, Belgium. desktop study Table 2: Table showing the real cases studied using different renewable energy and energy efficient systems. From the analysis of the monthly profiles for the energy demand and the real cases, a best practice system is proposed for each model district. Each best practice system includes an ambitious but realistic share of renewable energy, taking into account district restrictions, climatic conditions, and characteristics of each renewable technology. The best practice systems as well as the conventional systems (reference) for each model district are summarised in the next table.

Model district type 1 type 2A type 2B Description Urban or suburban, mixed use, Residential, Athens Residential, Helsinki SYSTEM CONSIDERED Best Practice including renewables Individual (R 2 ) and central condensing storage systems (NR), individual split heat pumps for cooling (R) and Central biomass fired boilers, Photovoltaics Central gas fired condensing boilers, solar thermal panels for DHW (R), individual split heat pumps for cooling (R), Photovoltaics Central biomass fired boilers, Urban Wind Turbines type 2C Residential, Central biomass fired boilers, Photovoltaics type 3 Business district/office park, Central condensing boilers, electrically heated storage systems and compression chillers. ATES (Aquifer Thermal Energy Storage)+ Large wind turbine(s) type 4 Multifunctional development centre, Combi-heat pumps (R), ATES (NR) + Urban Wind Turbines Table 3: Table summarising the reference system as well as a best practice system for each of the model districts. Assuming all renewable energy can be used within the district, the consumption of fossil fuels and electricity from grid, has been calculated for each of the model districts equipped with the best practice system. This energy consumption has been compared with the consumption of the reference installation. The results are shown in Table 4 below. 2 (R) = residential buildings, (NR) = non residential buildings

Model district Description SYSTEM CONSIDERED MDT1 2444981 type 1 Urban or suburban, mixed use, 179123 1498523 MDT 2A 688913 type 2A Residential, Athens 49781 486413 277937 MDT2B 1264216 type 2B Residential, Helsinki 483361 413588 MDT2C 182789 type 2C Residential, 488561 342311 MDT3 6871748 type 3 Business district/office park, 52367 2177947 326692 MDT4 type 4 Multifunctional development centre, 1149361 2493972 246952 Table 4: Estimation of the energy consumption when implementing best practice systems 89855

First estimations show that it is feasible, in each district, to achieve a reduction in primary energy consumption (from fossil fuels and grid electricity) in the range of 2-4%, leading to a corresponding reduction of CO 2 emissions. This is just a conservative estimation because at this stage it is not possible to estimate the effect of application of a smart control system (which is being developed in WP4) intended to match the demand and supply of energy. The reason is that at this stage of the project, it is difficult to quantify the effect of a smart control system with any level of accuracy. More detailed calculations of the extent, to which the introduction of renewables have an effect on energy, economy and ecology is the subject of Deliverable 2.4 E-Hub system impact calculation model.