Mainstreaming Energy Communities in the Transition to a Low-Carbon Future: A Methodological Approach
Abstract
:1. Introduction
- It is a legal entity and its functioning is regulated through its statutes;
- The assembly decides on everything and appoints a board of directors;
- The rule of “one member, one vote” is applied;
- Responsibility can be (and is almost always) limited, avoiding an intermingling with the shareholders’ personal assets;
- It is an organisation which, although it can make profits, has the primary aim of delivering benefits to its members, for example by providing goods and services on better terms than on the market or carrying out the activities of their corporate purpose;
- The number of members is variable, as is the capital, which simplifies membership entries and exits. In addition to the share capital, the shareholders can lend money to the company depending on the establishment of a social loan regulation. This activity is not considered to be a collection of savings from the public and is therefore not subject to capital market regulation rules;
- Citizens, as members of the cooperative, control the operations of the EC of which the cooperative is the owner or holds majority shares. Moreover, the citizens may also hold minority stakes in other companies.
- Facilitating consumers to become prosumers of RE, firstly in three pilot regions (Italy, Poland, and the Czech Republic), and secondly in cities across Europe after the pilot projects. This involves the application of Consumer Stock Ownership Plans (CSOPs), utilising established up-to-date best practice by inclusive financing techniques combined with energy efficiency measures.
- Encouraging local authorities and consumers, demonstrating the positive impact co-ownership has on consumer behaviour, and showing the ability of this democratic participation model to include women as well as those of low-income households, in particular the unemployed.
- Empowering consumers and municipalities in a capacity-building program through the launch of an interactive online “RE Prosumer Investment Calculator” and seminars in the five partner countries (Germany, Italy, Bulgaria, Poland, and the Czech Republic).
- Formulating policy recommendations to promote prosumership and to remove barriers for consumers to become active market players at the EU and national levels.
2. Methodological Framework
2.1. Phase I: Preparation
- (1)
- The first survey regards the investment identification of RESs, which is composed of five main sections [7]. This survey collects a general description of the buildings considered for each pilot study case, describing the current situation (i.e., geometry and energy plant systems) and the design one (i.e., planned project in terms of RES and financial aspects). The first section identifies the building characteristics (e.g., building ownership, building construction year, year of the last refurbishment, heat and domestic hot water (DHW) distribution system operator, average of consumption expenses, total number of dwellings or offices, total official number of inhabitants/employees, number of floors, total usable area, and total roof area). The second section investigates the existing conventional energy sources or external supplier (e.g., type of energy sources, installed power or purchased power if the district heating (DH) network is present). The third section describes the existing RESs, for example the type of energy sources and installed power. In the fourth part, the planned RESs are investigated. Finally, the fifth section is dedicated to the planned structure of financial sources for RES investment (e.g., type of financial sources and percentage of overall costs). Since the target is on a local scale, the definition of the building’s database is crucial.
- (2)
- The second survey reports the data in terms of energy costs and tariffs for the actual situation, for the use of non-renewable energy sources. The aim of this survey is to collect information about the use of non-renewable energy sources. Specifically, average consumption fee data (€/GJ) are reported (e.g., annual consumption (GJ), historical data for oil and natural gas cost (€/GJ), and the average fixed fee (€/month)).
2.2. Phase II: Preliminary and Feasibility Analysis
- (1)
- Energy impact assessment of the current situation, which determines the energy needs and energy uses for space heating, DHW, and lighting and equipment through collecting the measured data and in-situ analysis. Also, energy analysis has been assessed after implementing retrofitting measures through the building energy simulation model. At least two different refurbishment alternatives (for each case study) have been proposed. The retrofit alternatives concern the envelope system, the energy system installing RES, and the control system.
- (2)
- Environmental impact assessment illustrates the strategies to minimize the environmental impact with each alternative.
- (3)
- Economic and financial assessment of the investment costs.
2.3. Phase III: Target Group Involvement
- (1)
- Info events: Meetings with local institutions and organizations that work in the area in order to transmit the project objectives and dialogue on how to include citizens, without neglecting those belonging to vulnerable groups.
- (2)
- Workshops: This second method allowed us to inform invited citizens about a specific topic and create a semi-structured debate with them. Specifically, with the support of local authorities, known and recognized in the area, a diverse group of citizens were invited with the aim of giving them some fundamental notions about the project topic, such as the meaning of energy transition, the use of energy from renewable sources, the energy community, and the share ownership plan by consumers. At the same time, the educational moments were alternated with moments of learning verification through answers to questions or specific activities in order to express their thoughts and create a constructive debate. This is a semi-structured method in which people are free to express themselves.
- (3)
- Administering a specific questionnaire: through this method, the interviewees were asked to choose only one answer among those proposed; this method is more restrictive than the previous one. In particular, the results obtained in the “workshop meeting group” made it possible to define the questionnaire which in its final version is composed of five macro parts including detailed information:
- Attitude and willingness information: level of degree interest towards the EC project;
- Feeling related to community identity information: level of feeling related to trust, satisfaction, pride, hope, disgust, shame, fear, boredom;
- Technical information: building type and age, type of heating system, efficiency of the energy plant or building envelope;
- Socio-economic information: personal and family income, family composition, building construction year, and building ownership;
- Socio-demographic information: age, gender, education level, nationality, marital status, and municipality.
- The participation in decision-making is possible through the trustee, who represents the citizens interested in CSOP, while individual consumer-shareholders may execute control rights on a supervisory board or advisory council. Therefore, the model is of consumer-centred investment for general services, providing participation both financially and in regard to management decisions.
- Municipalities, small and medium-sized enterprises (SMEs) and other local stakeholders are permitted as co-investors. CSOPs avoid personal liability for consumer-shareholders.
- The Operating Society invests in new or existing RE plants and operates on behalf of different actors as co-owners.
- It is possible to demand loans from banks;
- New RE plants supply energy to consumers at fixed price and generate revenues from excess production sold to the grid.
3. Case Study
3.1. RESs in Susa Valley
3.2. Energy Poverty in Susa Valley
3.3. Implementing the EC Project in Susa Valley
4. Results and Discussions
4.1. Phase I: Preparation
4.2. Phase II: Preliminary and Feasibility Analysis
4.2.1. Preliminary Analysis (Energy Retrofit Alternatives)
- Significant energy leakage through the opaque casing (as shown by the values of thermic transmittance in Table 3);
- Obsolete regulation and balance systems (simple regulation on-off with no internal temperature compensation);
- Obsolete heat generation technology (oil boilers over 10 years old);
- Not clean energy sources (diesel fuel) and consequent high emission levels of CO2.
4.2.2. Feasibility Analysis (KPI Selection and Evaluation)
- ENV1—Primary energy saving. Primary energy that would be saved if the new plant was built. It is linked to the renewable nature of the investment and to the interventions on the building envelope. It was calculated with a specific software in which the material, thickness, thermic transmittance, and internal surface resistance were some of the inputs needed [9].
- ENV4—Local PM10 emission reduction. PM10 emissions are caused by fuel burning and heavy industrial processes and are very harmful to human health [18]. These emissions cause lung diseases, heart attacks and arrhythmias, cancer, atherosclerosis, childhood respiratory disease, and premature death.
- EC1—Payback period (PBP). PBP, simple or discounted, is a popular criterion that represents the time in which negative and positive cash flows are equal. It represents the moment after which the expenses are amortized and there is the actual gain. This criterion gives immediate insight to investors in the event that there is a preference to shorten the PBP [20]. The payback period is assessed as shown in Equation (1):
- EC2—Investment cost. Many studies consider investment costs as the most important criterion to evaluate energy savings interventions. The investment cost involves all the costs related to refurbishment of the building and/or new heating system; it includes the purchase of building material, technological installations, manpower, and set up of the cost for each individual element of the renovation project (building envelope and energy systems), as demonstrated in Table 11 [21,22].
- EC3—Public incentives. This is the percentage of savings linked to the share of investment cost covered by administrative incentives. The Stability Law confirmed the extension of 65% tax reductions for energy efficiency measures and 50% for restructuring buildings completed by the end of 2017 [23]. “Conto Termico” involves the following incentives:
- Up to 65% of the expenditure incurred for nearly Zero Energy Buildings (nZEBs);
- Up to 40% for wall and ceiling insulation, replacement of windows, solar shading, indoor lighting, building automation technologies, boilers;
- Up to 50% for thermal insulation work in climate zones E/F and up to 55% in case of thermal insulation and replacement of window seals when combined with other interventions (heat pumps, solar thermal, etc.).
- EC4—Savings on energy expenditure. The savings on annual expenditure taking into account the primary energy savings calculated previously.
- EC5—Labour cost. It includes the salary of employees who are directly involved in production activities, services (such as general repairs and maintenance performance), and supervision. It is assumed to be 40% of investment costs, as an expert in the field suggested during an internal meeting [24,25].
- EC6—Labour cost by a social cooperative. The part of labour cost which will be covered by the social cooperative.
- EC7—Material cost. The costs of raw materials or parts that go directly into producing products or providing services. This cost was assumed to be only at the beginning of the project (one off) including aspects like the boiler, insulation, and concrete.
- EC8—Material cost purchased on the territory. This criterion evaluates the portion of material cost that remains in the territory. The territory is intended to be the Susa Valley.
- EC9—Running cost. This involves the energy costs plus maintenance costs. The maintenance costs are assumed to be 2% of investment cost according to [26].
- EC10—Type Thermal Account Access (TAA) vs. Energy Efficiency Certificates (EEC). This represents the access to the thermal account and energy efficiency certificates, Italian public incentives carried out by energy services management.
- T1—Increase of plant system efficiency. This is the increase in the efficiency of the new system plant compared to the existing one [9].
- T2—Installed power reduction. This represents the reduction of installed power; it is always an aspect that contributes directly in energy reduction.
- S1—Architectural impact. This indicator evaluates the visual outcome that may be created by the application of retrofitting measurements for a city. When retrofit measures lead to aesthetic improvement of the city, this criterion has a higher value. Five scores of impact are presented in Table 12 according to the study conducted by Dall’O’ et al. [27], with reference to specific measures. This criterion adopts an ordinal scale to rank the strategies, from the best to the worst.
4.2.3. Feasibility Analysis (Best Scenario Selection)
- Each environmental indicator will get a weight of 0.0625 percent, obtained through the division of 25 percent by four indicators.
- Each economic indicator will get a weight of 0.025 percent, obtained through the division of 25 percent by 10 indicators.
- Each technical indicator will get a weight of 0.125 percent, obtained through the division of 25 percent by two indicators.
- Each social indicator will get a weight of 0.25 percent, obtained through the division of 25 percent by one indicator.
- 23.5 percent for environmental indicators;
- 11.8 percent for technical indicators;
- 5.9 percent for social indicators; and
- 58.8 percent for economic indicators
- 30 percent for the environmental category and 0.075 percent for each environmental indicator;
- 30 percent for the economic category and 0.03 percent for each economic indicator;
- 20 percent for the technical category and 0.1 percent for each technical indicator; and
- 20 percent for the social category and 0.2 percent for each social indicator
4.3. Phase III: Target Group Involvement
4.3.1. Info-Events
4.3.2. Workshops
“What type of heating system do you have in your home? What are the costs? Are you satisfied with your system? Do you think your heating bill is too high? Are you having problems keeping your home adequately heated?”
- Distrust because, being an innovative project, there is no one who can guarantee that the project will be successful. In this case no one can give feedback on the success of this type of project;
- Control and verification due to the disparity of investment of the various actors. This is to avoid situations of greater representation with greater investment;
- Bureaucracy: navigating the process and the necessary documentation could be complicated for simple citizens not working in the legal field.
5. Conclusions and Future Developments
Author Contributions
Funding
Acknowledgments
Conflicts of Interest
References
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No. | Municipality (City) | Number | Building | Existing Energy Sources for Heating | Type of Installation |
---|---|---|---|---|---|
1 | Oulx | 1.a | School and gym | Oil and natural gas boiler (individual generators) | DH network (biomass) |
1.b | Nursery | ||||
1.c | Gym | ||||
1.d | Municipality | ||||
1.e | Touristic office | ||||
1.f | Social activity building | ||||
1.g | Building (residential) | ||||
2 | Novalesa | 2.a | Abbey | Oil and LGP boiler (individual generators) | DH network (biomass) |
2.b | Private building 1 | ||||
2.c | Private building 2 | ||||
3 | Rueglio | 3.a | Municipality | Oil boiler (individual generators) | DH network (biomass) |
3.b | Retirement house | ||||
4 | San Giorio di Susa (building scale) | 4.a | Multi-use room and bar | Natural gas boiler (individual generators) | DH network (biomass) |
5 | San Giorio di Susa (city scale) | 5.a | Private residential buildings | Individual oil stove | DH network (biomass) |
6 | Villar Dora | 6.a 6.b | School and gym Kindergarten | Natural gas boiler | DH network (biomass) and solar thermal collectors |
7 | Susa | 7.a | DH network | Oil and natural gas boiler (individual generators) | DH network (biomass) |
8 | Bardonecchia | 8.a | DH network | Oil and natural gas boiler (individual generators) | DH network (biomass) |
9 | Bussoleno | 9.a | DH network | Natural gas boiler (individual generators) | DH network (biomass) |
10 | Almese | 10.a | Sport (facilities) buildings | Natural gas boiler (individual generators) | DH network (biomass) |
10.b | Middle school | ||||
10.c | Private buildings |
No. | Ownership and Function | Construction Year | Latest Refurbishment Year | Average Heat and DHW Expenses (€/year) | Total Number of Zones | Total Number of Users | Total Usable Area (m2) | Average Annual Consumption (MWh) |
---|---|---|---|---|---|---|---|---|
1.a * | Public; non-residential (educational) | 1958 | 2018 (seismic) | 57,915 | 27 | 250 | 2800 | 300 |
1.b * | Public; non-residential (educational) | 1988 | none | 5585 | 1 | 50 | 270 | |
1.c * | Public; non-residential (sportive) | NA | NA | NA | 1 | 220 | NA | |
1.d | Public; non-residential (administrative) | 1980 | 2016 (windows) | 13,831 | 10 | 26 | 660 | 150 |
1.e | Public; non-residential (services) | 1995 | none | 14,669 | 3 | 6 | 700 | 150 |
1.f | Public; non-residential (services) | First years of 1900 | 2016 (structural) | 3,000 | 3 | 2 | 300 | 30 |
Before | ||
---|---|---|
Element | Thickness (mm) | Thermic Transmittance (W/m2K) |
School external wall | 400 | 0.847 |
Gym external wall | 290 | 1.020 |
Nursery external wall | 70 | 0.332 |
School upper-attic slab | 200 | 2.401 |
Gym upper-attic slab | 60 | 1.429 |
Nursery upper-attic slab | 50 | 0.438 |
Client | Cost | Years |
---|---|---|
Middle school | €46,857 | 2012 |
Elementary school | €17,620 (average) | 2003–2012 |
Nursery | €5,050 | 2013 |
Zone | Day of Utilization | Hours per Day | Internal Temperature Point Set When Used/Not Used |
---|---|---|---|
School | 5 | 12 | 20 °C/16 °C |
Gym | 7 | 12 | 20 °C/16 °C |
Nursery | 5 | 12 | 22 °C/19 °C |
Service | Qp,nren (kWh) | Qp,ren (kWh) | Qp,tot (kWh) | EP,nren (kWh/m2) | EP,ren (kWh/m2) | EP,tot (kWh/m2) |
---|---|---|---|---|---|---|
Heating | 491,432 | 0 | 491,432 | 172.98 | 0.0 | 172.98 |
Domestic hot water | 37,919 | 0 | 37,919 | 13.35 | 0.0 | 13.35 |
TOTAL | 529,350 | 0 | 529,350 | 186.32 | 0.0 | 186.32 |
Code of Simulation | Interventions |
---|---|
0.0 | As-built simulation model. |
0.1 | As-built simulation model from real consumption (benchmark). |
A1 | Simulation 0 and replacement of the boilers with a unique biomass-fired one and regulation retrofitting. |
A2 | Simulation 1 and the upper-attic slab insulation (18 cm). |
A3 | Simulation 2 and external walls insulation for the school and the gym (18 cm). |
A4 | Simulation 1 and nZEB conditions obtained with the upper-attic slab insulation (40 cm), external walls insulation for the school and the gym (30 cm), and the nursery’s external walls (25 cm). |
The A5 | Simulation 1 and nZEB conditions obtained with the upper-attic slabs insulation (50 cm for the school and the gym, 40 cm for the nursery), external walls insulation for the school and the gym (40 cm), and the nursery’s external walls as built. |
A6 | Simulation 1 and nZEB conditions obtained with the replacement of the windows with more efficient components (transmittance: <1.0 W/m2K), upper-attic slab insulation (15 cm for the school and the gym, 12 cm for the nursery), external wall insulation for the school and the gym (15 cm), and the nursery’s external walls as built. |
After * | ||
---|---|---|
Element | Thickness (mm) | Thermic Transmittance (W/m2K) |
School external wall | 720 | 0.110 |
Gym external wall | 610 | 0.112 |
Nursery external wall | 320 | 0.103 |
School upper-attic slab | 600 | 0.084 |
Gym upper-attic slab | 460 | 0.082 |
Nursery upper-attic slab | 450 | 0.073 |
Code of Simulation | Qp,tot | Qp,ren | Qp,nren | CO2 Emissions | |||
---|---|---|---|---|---|---|---|
(kWh/y) | (kWh/y) | % (ren/tot) | (kWh/a) | % (nren/tot) | (kgCO2eq/a) | % (VS 0.1) | |
0.0 | 529,350 | - | - | 529,350 | 100% | 137,551 | 85.84% |
0.1 | 616,697 | - | - | 549,061 | 100% | 160,248 | 100% |
A1 | 457,140 | 365,712 | 80% | 91,428 | 20% | 22,857 | 14.26% |
A2 | 335,284 | 268,228 | 80% | 67,057 | 20% | 16,764 | 10.46% |
A3 | 197,529 | 158,023 | 80% | 39,506 | 20% | 9876 | 6.16% |
A4 | 177,276 | 141,821 | 80% | 35,455 | 20% | 8864 | 5.53% |
A5 | 177,213 | 141,771 | 80% | 35,443 | 20% | 8861 | 5.53% |
A6 | 177,638 | 142,110 | 80% | 35,528 | 20% | 8882 | 5.54% |
Category | Code | Indicator | Type | Data Source | Unit |
---|---|---|---|---|---|
Environmental | ENV1 | Primary energy saving | Quantitative | Estimated or metered data | (kWhprimary energy/year) |
ENV2 | Global CO2 emission reduction | Quantitative | Estimated or metered data | (kg/year) | |
ENV3 | Local NOX emission reduction | Quantitative | Estimated or metered data | (kg/year) | |
ENV4 | Local PM10 emission reduction | Quantitative | Estimated or metered data | (kg/year) | |
Economic | EC1 | Payback period (PBP) | Quantitative | Calculation | (Years) |
EC2 | Investment cost | Quantitative | Calculation | (Euro) | |
EC3 | Public incentives | Quantitative | Process documentation | (%) | |
EC4 | Savings on energy expenditure | Quantitative | Calculation | (Euro/year) | |
EC5 | Labour cost | Quantitative | Estimated or metered data | (Euro/year) | |
EC6 | Labour cost by a social cooperative | Quantitative | Estimated or metered data | (Euro/year) | |
EC7 | Material cost | Quantitative | Estimated or metered data | (Euro) | |
EC8 | Material cost purchased on the territory | Quantitative | Estimated or metered data | (Euro) | |
EC9 | Running cost | Quantitative | Calculation | (Euro/year) | |
EC10 | Type thermal account access (TAA) vs. Energy efficiency certificates (EEC) | Qualitative | Process documentation | (TAA/EEC) | |
Technical | T1 | Increase of plant system efficiency | Quantitative | Estimated or metered data | (%) |
T2 | Installed power reduction | Quantitative | Estimated or metered data | (kW) | |
Social | S1 | Architectural impact | Qualitative | Process documentation | (Ordinal) |
Materials/Service | Price (€/Unit) | Quantity (Unit) | Amount (€) |
---|---|---|---|
Wall insulation | 100 | 2,000 | 200,000 |
Upper-attic insulation | 100 | 1,200 | 120,000 |
audits | 6250 | 1 | 6250 |
Building site | 20,000 | 1 | 20,000 |
Lean concrete | 2500 | 1 | 2500 |
Foundation | 15,000 | 1 | 15,000 |
Walls | 3750 | 4 | 15,000 |
Slab | 12,500 | 1 | 12.500 |
Waterproofing | 1000 | 1 | 1000 |
Passages | 5000 | 1 | 5000 |
District pipes | 20,000 | 1 | 20,000 |
Biomass boiler | 70,000 | 1 | 70,000 |
Plant modifications | 10,000 | 4 | 40,000 |
Control | 20,000 | 1 | 20,000 |
Mounting | 30,000 | 1 | 30,000 |
Project | 20,000 | 1 | 20,000 |
Tele management | 20,000 | 1 | 20,000 |
TOTAL | 617,250 |
Typology of Criterion | Description of Criterion | Numerical Value of Criterion | Description of Intervention |
---|---|---|---|
Positive | Great positive impact | 1 | External Thermal Insulation Composite Systems |
Positive impact | 2 | Windows replacement | |
Neutral | No impact | 3 | Roof insulation – Boiler replacement – Lightning replacement |
Negative | Little negative impact | 4 | Photovoltaic panels |
Negative impact | 5 | Solar thermal collector |
Category | Indicator | A1 | A2 | A3 | A4 | A5 | A6 | |||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
Environmental | ENV1 (kWhprimary energy/year) | 525,269 | 549,640 | 577,191 | 581,242 | 581,254 | 581,169 | |||||
ENV2 (kg/year) | 137,427 | 143,520 | 150,408 | 151,420 | 151,423 | 151,402 | ||||||
ENV3 (kg/year) | 94.55 | 98.94 | 103.89 | 104.62 | 104.63 | 104.61 | ||||||
ENV4 (kg/year) | 6.83 | 7.15 | 7.50 | 7.56 | 7.56 | 7.56 | ||||||
Economic | EC1 (PBP) (years) | 8.3 | 11.7 | 16.5 | 16.3 | 16.3 | 16.3 | |||||
EC2 (Euro) | 284,750 | 417,250 | 617,250 | 617,250 | 617,250 | 617,250 | ||||||
EC3 (%) | 40% | 40% | 40% | 65% | 65% | 65% | ||||||
EC4 (Euro/year) | 34,142 | 35,727 | 37,517 | 37,781 | 37,782 | 37,776 | ||||||
EC5 (Euro/year) | 136,250 | 136,250 | 136,250 | 136,250 | 136,250 | 136,250 | ||||||
EC6 (Euro/year) | 34,063 | 34,063 | 34,063 | 34,063 | 34,063 | 34,063 | ||||||
EC7 (Euro) | 148,500 | 281,000 | 481,000 | 481,000 | 481,000 | 481,000 | ||||||
EC8 (Euro) | 51,975 | 98,350 | 168,350 | 168,350 | 168,350 | 168,350 | ||||||
EC9 (Euro/year) | 39,523 | 33,156 | 26,962 | 25,630 | 25,459 | 25,490 | ||||||
EC10 (TAA/EEC) | TAA | TAA | TAA | TAA | TAA | TAA | ||||||
Technical | T1 (%) | 9.80% | 9.80% | 9.80% | 9.80% | 9.80% | 9.80% | |||||
T2 (kW) | 175 | 175 | 175 | 175 | 175 | 175 | ||||||
Social | S1 (-) | 3 | 1 | 1 | 1 | 1 | 2 |
ENV1 | ENV2 | ENV3 | ENV4 | T1 | T2 | S1 | |||||
Baseline | w | 0.0625 | 0.0625 | 0.0625 | 0.0625 | 0.125 | 0.125 | 0.25 | |||
p | 21,397 | 5349 | 3.85 | 0.28 | 9.8 | 175 | 0.76 | ||||
Change 1 | w | 0.059 | 0.059 | 0.059 | 0.059 | 0.059 | 0.059 | 0.059 | |||
p | 21,397 | 5349 | 3.85 | 0.28 | 9.8 | 175 | 0.76 | ||||
Change 2 | w | 0.075 | 0.075 | 0.075 | 0.075 | 0.1 | 0.1 | 0.2 | |||
p | 21,397 | 5349 | 3.85 | 0.28 | 9.8 | 175 | 0.76 | ||||
EC1 | EC2 | EC3 | EC4 | EC5 | EC6 | EC7 | EC8 | EC9 | EC10 | ||
Baseline | w | 0.025 | 0.025 | 0.025 | 0.025 | 0.025 | 0.025 | 0.025 | 0.025 | 0.025 | 0.025 |
Change 1 | p | 1.66 | 179,387 | 13 | 3637 | 41,397 | 10,349 | 137,990 | 48,296 | 8627 | 1 |
Change 1 | w | 0.059 | 0.059 | 0.059 | 0.059 | 0.059 | 0.059 | 0.059 | 0.059 | 0.059 | 0.059 |
Alternative | A1 | A2 | A3 | A4 | A5 | A6 |
---|---|---|---|---|---|---|
Net phi | −0.3156 | 0.0020 | 0.0514 | 0.1042 | 0.1043 | 0.0538 |
Rank | 6 | 5 | 4 | 2 | 1 | 3 |
Alternative | A1 | A2 | A3 | A4 | A5 | A6 |
---|---|---|---|---|---|---|
Net phi | −0.0516 | 0.0208 | −0.0629 | 0.0353 | 0.0354 | 0.0230 |
Rank | 5 | 4 | 6 | 2 | 1 | 3 |
Alternative | A1 | A2 | A3 | A4 | A5 | A6 |
---|---|---|---|---|---|---|
Net phi | −0.2923 | −0.0158 | 0.0384 | 0.1032 | 0.1034 | 0.0631 |
Rank | 6 | 5 | 4 | 2 | 1 | 3 |
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Torabi Moghadam, S.; Di Nicoli, M.V.; Manzo, S.; Lombardi, P. Mainstreaming Energy Communities in the Transition to a Low-Carbon Future: A Methodological Approach. Energies 2020, 13, 1597. https://doi.org/10.3390/en13071597
Torabi Moghadam S, Di Nicoli MV, Manzo S, Lombardi P. Mainstreaming Energy Communities in the Transition to a Low-Carbon Future: A Methodological Approach. Energies. 2020; 13(7):1597. https://doi.org/10.3390/en13071597
Chicago/Turabian StyleTorabi Moghadam, Sara, Maria Valentina Di Nicoli, Santiago Manzo, and Patrizia Lombardi. 2020. "Mainstreaming Energy Communities in the Transition to a Low-Carbon Future: A Methodological Approach" Energies 13, no. 7: 1597. https://doi.org/10.3390/en13071597
APA StyleTorabi Moghadam, S., Di Nicoli, M. V., Manzo, S., & Lombardi, P. (2020). Mainstreaming Energy Communities in the Transition to a Low-Carbon Future: A Methodological Approach. Energies, 13(7), 1597. https://doi.org/10.3390/en13071597