The <str<strong>on</strong>g>12th</str<strong>on</strong>g> <str<strong>on</strong>g>Internati<strong>on</strong>al</str<strong>on</strong>g> <str<strong>on</strong>g>Symposium</str<strong>on</strong>g> <strong>on</strong> <strong>District</strong> <strong>Heating</strong> <strong>and</strong> <strong>Cooling</strong>,September 5 th to September 7 th , 2010, Tallinn, Est<strong>on</strong>iatransport systems. At preset there exists no easyaccessible calculati<strong>on</strong> method.Different countries have different energy chains <strong>and</strong>energy supply systems. Analysis of even the mostactual processes <strong>and</strong> process lines does not existneither for Norway or Europe [12] – [13]. In order tocompare <strong>and</strong> choose different energy chain there is aneed for st<strong>and</strong>ardized methods. The lack of objective<strong>and</strong> reliable data of the different elements in the energychain might prevent an efficient use of energy, <strong>and</strong>c<strong>on</strong>tributes to wr<strong>on</strong>g choices <strong>and</strong> unnecessary CO 2emissi<strong>on</strong>s. [14] – [15].The method is principally described in EN 15603 [2]<strong>and</strong> provides <strong>on</strong>ly single PEF values for 9 energycarriers <strong>and</strong> 4 energy chains, <strong>and</strong> is based <strong>on</strong> averageEuropean values. Without an easy accessible methodor methods is it not possible to compare PEF values<strong>and</strong> calculate the actual envir<strong>on</strong>mental impact ofdifferent energy chains. Some studies [16] -[21] havedescribed parts of this topic, but they lack a holisticview of the energy chains from cradle to grave, oftenthe chosen system boundaries are different, time scalevaries, detailing level different <strong>and</strong> the, approach/method varies. Results from different studies thereforeare not comparable.Why is it importantPEF is a key indicator to be able to evaluate energyuse (for different purposes) especially with regards tothe goals of the EPBD [1]. PEF is an over all energyefficiency indicator which makes it possible to compare<strong>and</strong> collocate different energy sources <strong>and</strong> energycarriers by a single number. The same method can beused to calculate the CO 2 emissi<strong>on</strong>.What have others d<strong>on</strong>e?Different CEN st<strong>and</strong>ards describe, <strong>and</strong> partly discuss,the theory. In the EC-m<strong>and</strong>ated CEN st<strong>and</strong>ards relatedto EPBD mainly <strong>on</strong>e single reference are referred [14]whilst the PEF values have been gradually changedover time. An extended literature survey has showeddisc<strong>on</strong>tinuity between some of the studies performed<strong>and</strong> lack of details in the calculati<strong>on</strong>s.Methods developed to provide PEF values for heatingsystems in buildings might be useful, but they will nottotally comply with a whole energy chain approach. LifeCycle Assessment (LCA) might also c<strong>on</strong>tribute to ageneric method, but the vast number of inputparameters, often more than 6000 in a traditi<strong>on</strong>ally LCAdem<strong>on</strong>strates the need for a more easy accessiblemethod.What must be d<strong>on</strong>e?In order to develop a method a systems engineeringapproach will be used. The most important task in thisc<strong>on</strong>text is the identificati<strong>on</strong> of relevant energy systems33<strong>and</strong> process lines (chains) primary in Norway <strong>and</strong> theNordic countries. Detailed data must be provided suchas efficiency <strong>and</strong> loss from the different systems <strong>and</strong>mix of systems, or at least provide the necessaryparameters. Since the systems engineering approachis chosen, the problem approach must be defined, atheoretical method developed <strong>and</strong> data collect. Thisincludes performing of a trade-off between thetheoretical model <strong>and</strong> available informati<strong>on</strong>. Themethod shall be tested by selected case studies <strong>and</strong>finally adjusted.Main hypothesisAs a part of the systems engineering process, <strong>on</strong>e orseveral (systems engineering) hypothesis is developed.The success of a system engineering process isrelated to the fulfilment of the hypothesis. In this projectthe system engineering method must prove two mainhypotheses;1. It is possible to develop a generic method thatprovides credible data for calculating primaryenergy use by use of PEF values.2. It is possible to apply the generic method <strong>on</strong>energy systems in the Nordic regi<strong>on</strong> for CHPplants utilising bio based fuel.Stakeholder analysisA stakeholder is a party having a right, share or claimin the system [16]. The intenti<strong>on</strong> with the stakeholderanalysis is to reveal the different kinds of stakeholderssince they might have requirements influencing apossible method in a legal way. Stakeholders withmutual interest are aggregated in groups; some ofthem might not be in incompliance with each other.Energy producer, distributors, energy companies;Business profitability is the main issue byoptimizing producti<strong>on</strong> from different energy carriersaccording to cost-benefitInvestors (energy <strong>and</strong> building); The electricitymarkets are opening gradually throughout Europe,e.g. Nord Pool Financial Marked <strong>and</strong> investmentsin Power producti<strong>on</strong> <strong>and</strong> the introducti<strong>on</strong> of socalled Green Electricity Certificates might be a newor extended business area. Investors in thebuilding marked might be interested in the actualPEF values <strong>and</strong> primary energy use whenchoosing between different investment objects.Building owners, end user; Correct calculati<strong>on</strong> ofPEF values <strong>and</strong> primary energy use is supposed tohave significant importance for the choice ofenergy supply system, building services, insulati<strong>on</strong>level, especially for new buildings <strong>and</strong> majorrehabilitati<strong>on</strong> projects. Future operating cost might
The <str<strong>on</strong>g>12th</str<strong>on</strong>g> <str<strong>on</strong>g>Internati<strong>on</strong>al</str<strong>on</strong>g> <str<strong>on</strong>g>Symposium</str<strong>on</strong>g> <strong>on</strong> <strong>District</strong> <strong>Heating</strong> <strong>and</strong> <strong>Cooling</strong>,September 5 th to September 7 th , 2010, Tallinn, Est<strong>on</strong>iadepend of PEF since taxes might be dependant ofthe primary energy use <strong>and</strong>/or the CO 2 emissi<strong>on</strong>.Developers& Building <strong>and</strong> c<strong>on</strong>structi<strong>on</strong> industry;Technical equipment in the building <strong>and</strong> designstrategies depends <strong>on</strong> the actual use of thespecific energy carrier. The use of PEF values inthe primary energy calculati<strong>on</strong>s might change thevalue of traditi<strong>on</strong>ally installed equipment due tooverall energy costs <strong>and</strong> also create a dem<strong>and</strong> formore energy flexible soluti<strong>on</strong>s.Politicians, government, Regulators, Communityplanning; Most European countries have affiliatedthe Kyoto Protocol, <strong>and</strong> a possible method toincrease the use of renewable energy policy tools<strong>and</strong> subsidy schemes might be based <strong>on</strong> the useof PEF values for the different soluti<strong>on</strong>s, besidespossible tax <strong>on</strong> systems with high primary energyuse.Nati<strong>on</strong>al regulators m<strong>and</strong>atory m<strong>on</strong>itor <strong>and</strong> reportemissi<strong>on</strong> levels <strong>and</strong> this influences nati<strong>on</strong>allegislati<strong>on</strong>, local <strong>and</strong> urban planningResearch groups, Universities; Different researchcommunities might be interested in development ofother PEF calculati<strong>on</strong> methods or adjustments ofmethods <strong>and</strong> development of new soluti<strong>on</strong>s <strong>and</strong>systemsDESCRIPTION OF MEASURES OF EFFECTIVENESSAs earlier stated the measures of effectiveness (MOE)should be independent of any soluti<strong>on</strong>s <strong>and</strong> notc<strong>on</strong>cerned with internal details [22]. It might also befruitful to develop MOE for the different kind ofstakeholders since they often might have a differentopini<strong>on</strong> regarding MOE.In this c<strong>on</strong>text MOE are primarily described for the<strong>on</strong>going Nordic PhD-project Primary Energy Efficiency(PEE). A further detailing level, by including thestakeholders, might provide valuable informati<strong>on</strong>, butthat is c<strong>on</strong>sidered to lie outside the scope of this work.The methods (tools) developed during the projectshould be suitable for different kind of energy chains.The results should be utilised by the differentkinds of stakeholders e.g. the building owner, thearchitect/designers of the building, the energysupplier <strong>and</strong> producer <strong>and</strong> finally politicians <strong>and</strong>governments.The methods will enable the different stakeholdersto choose between different energy systems <strong>and</strong>furthermore be able to reduce primary energy use<strong>and</strong> CO 2 emissi<strong>on</strong>s from stati<strong>on</strong>ary energypurposes.34INFORMATION MODELSThe requirement traceability informati<strong>on</strong> modelIn systems engineering shall the requirementtraceability informati<strong>on</strong> model “aim to show the breakdown of requirements from source documents to finalallocati<strong>on</strong> functi<strong>on</strong>s to stakeholders ―[2]This model is an important tool to keep track of thedifferent requirements, source documents <strong>and</strong>eventually what the system accomplishes <strong>and</strong> who orwhat are in charge. Usually an Entity-Relati<strong>on</strong>ship-Attribute method is used [23], where the entities(objects) represent the legislati<strong>on</strong>, requirements, etc.whilst the relati<strong>on</strong>ship shows the associati<strong>on</strong> betweenthe system/process.Planning <strong>and</strong>Building ActSourceBuildingregulati<strong>on</strong> TEKSourceBuilding GuideRENSourceSpecifieNS3031 sfuncti<strong>on</strong>AllocatedBuilding Permit tostakeholderDocumentsIncorporatesWorking Envir<strong>on</strong>m. ActSourceEN 15316-4-4:2007)SourceEPBD EnergyPerformance.SourceËN 15603:2007SourceL<strong>and</strong>fill DirectiveDocumentsSpecifieDisharge permit sRequirementsAllocated toSourceWaste regulati<strong>on</strong>sSourceNOx emissi<strong>on</strong>sBoilerFigure 3 Selected part of the requirement traceabilitymodel, case Norway96/62/ECAmbient AirSourceQualityDocuments1999/30/EC LimitvaluesRequirementsNOx…IncorporatesPolluti<strong>on</strong> C<strong>on</strong>trolActRequirementsSpecifiesDischarge permitRequirementsSpecifiesInternal c<strong>on</strong>trolsystemfuncti<strong>on</strong>Allocated toNOx emissi<strong>on</strong>1.2.2.1StakeholderMost EC directives are enforced <strong>and</strong> implemented inlaws, directi<strong>on</strong>s, regulati<strong>on</strong>s <strong>and</strong> guidelines, both in theEU <strong>and</strong> associated EEC countries, hence the order ofentities in Figure 3. Several directives influence thenati<strong>on</strong>al laws <strong>and</strong> regulati<strong>on</strong>s. Since the directivesusually are enforced through nati<strong>on</strong>al laws, the lawincludes requirements from more than <strong>on</strong>e directive likethe Norwegian Planning <strong>and</strong> Building Act [26], whichincludes requirements from EPBD [27], Directive <strong>on</strong> thepromoti<strong>on</strong> of the use of energy from renewable sources[30], Directive <strong>on</strong> the l<strong>and</strong>fill of waste [29], ThePolluti<strong>on</strong> C<strong>on</strong>trol Act [30] am<strong>on</strong>gst others.The requirements traceability model provides importantinformati<strong>on</strong> about c<strong>on</strong>straints regarding an energychain. Some of the elements such as the the WorkingEnvir<strong>on</strong>ment Act [31] might seem irrelevant, but theregulati<strong>on</strong>s set limits for the pollutant inside the workingarea, introducing need for e.g. c<strong>on</strong>veyor belts.Each functi<strong>on</strong> c<strong>on</strong>sists of several entities for instancethe discharge permit from regulators like TheNorwegian Climate <strong>and</strong> Polluti<strong>on</strong> Agency will setrestricti<strong>on</strong>s <strong>on</strong> the authorised discharge levels ofdifferent gasses not <strong>on</strong>ly NOx as illustrated in theFigure 3.
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academic access is facilitated as t
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