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>iaare c<strong>on</strong>sidered not to cause sulphur corrosi<strong>on</strong>problems, especially not with low-sulphur wood fuels.Certainly this design specificati<strong>on</strong> must be rec<strong>on</strong>sideredin case of changed fuel properties.The maximum pyrolysis producti<strong>on</strong> for each load pointis restricted by the maximum steam extracti<strong>on</strong> rate <strong>and</strong>by the boiler‘s maximum burning power. The maximumpossible pyrolysis yield logically requires highestpossible fuel input since heat must be provided both, fordrying <strong>and</strong> pyrolysis. C<strong>on</strong>versely, this means that thesteam enthalpy exceeds the dem<strong>and</strong> of the DHN. Thisis because the boiler temperature is c<strong>on</strong>trolled bymeans of the evaporator- <strong>and</strong> superheater tubes in theboiler walls. If now, the heat input in the boiler is kept <strong>on</strong>a higher level as usual the water amount needed todissipate the heat from the boiler walls is <strong>on</strong>lydecreasing to a certain amount (resulting from areduced temperature after the ec<strong>on</strong>omizer).C<strong>on</strong>sequently, in order to match the DH load, this heatmust now be ―dissipated‖ in the pyrolysis heatexchanger (19) or in the dryer (24). By iterati<strong>on</strong> the DHload is matched by adjusting dryer load, correlated splitoffto the pyrolysis heat exchanger <strong>and</strong> fuel input. In allcases the boiler load (characterised by the fuel heatinput) is restricted to 100%. So, the overload back-upcapacity of the boiler is maintained. With this setup thepyrolysis yield c<strong>on</strong>stantly increases with the decrease ofthe DH levels down to 60%. The maximum flow off thedryer (<strong>and</strong> thus its capacity) is be restricted by thepressure prevailing in the feedwater tank, which in turnis given by the extracti<strong>on</strong> pressure after the turbinestage (11). The pressure decreases with falling livesteam parameters <strong>and</strong> steam massflow. Hence, there isa pressure dependant maximum enthalpy flow that canbe fed into the feedwater tank until saturati<strong>on</strong> state isreached for the mixture of the c<strong>on</strong>densates from the DHexchanger (13) <strong>and</strong> the dryer (24). In order to overcomethis restricti<strong>on</strong> the feedwater tank pressure has beenincreased load-dependently to a maximum of 2 barsmatching its design pressure. However, due to thereas<strong>on</strong> menti<strong>on</strong>ed above, for loads below 60% the heatthat would need to be ―dissipated‖ in the dryer (in orderto match the DH load) would result in such a high dryerc<strong>on</strong>densate heat flow which again would bring thefeedwater bey<strong>on</strong>d saturati<strong>on</strong> state. Hence for thosecases the boiler load is gradually decreased, resulting inlower pyrolysis yields. The lowest DH load level that canbe represented is 28.6% of the plant‘s full load.Compared to a minimum load of 50% in the base case– which is given by the minimum fuel input required forstable combusti<strong>on</strong> c<strong>on</strong>diti<strong>on</strong>s in the boiler-, theintegrated process offers possibilities to increase theoperating hours of the CHP plant c<strong>on</strong>siderably.Fig. 2: CHP Plant with integrated pyrolysis <strong>and</strong> steam drying171
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>iaAPPLICATION OF THE PRIMARY ENERGYCONCEPT ACCORDING TO EN 15603Primary Energy C<strong>on</strong>ceptThe EU st<strong>and</strong>ard EN 15603 [2] h<strong>and</strong>les the energyperformance of a building as a whole <strong>and</strong> givesguidelines how energy use <strong>and</strong> producti<strong>on</strong> of a buildingshall be calculated. In order to aggregate the differentforms of energy produced <strong>and</strong> used within the building,primary energy (PE) <strong>and</strong> CO 2 emissi<strong>on</strong>s areaccumulated <strong>and</strong> expressed by means of primaryenergy factors (PEF) <strong>and</strong> CO 2 emissi<strong>on</strong> coefficients,respectively. PE is energy that has not been subjectedto any c<strong>on</strong>versi<strong>on</strong> or transformati<strong>on</strong> process [2]; it ishence not yet extracted from the source. In the PEapproach described in EN 15603, all energy carriersinvolved in the generati<strong>on</strong> process are retraced to theirsources <strong>and</strong> all energy needed to deliver the finalenergy product are aggregated to the total PEc<strong>on</strong>sumpti<strong>on</strong> <strong>and</strong> CO 2 emissi<strong>on</strong>s. Thus the PEapproach applies the holistic principles of life cycleassessment to an energy rating procedure. By retracingenergy c<strong>on</strong>sumpti<strong>on</strong> to the source, the systemboundaries automatically include the whole world, <strong>and</strong>thus depict the real impact of the system c<strong>on</strong>cerningenergy c<strong>on</strong>sumpti<strong>on</strong> <strong>and</strong> CO 2 emissi<strong>on</strong>s.In the power b<strong>on</strong>us method f El. is defined as the PEF ofthe electricity that is thought to be replaced by thepower generated in the CHP plant (for instance, in thisstudy the average power generati<strong>on</strong> efficiency inFinl<strong>and</strong> is used). This allocati<strong>on</strong> pays attenti<strong>on</strong> to thefact that the co-generated electricity is more sustainabledue the CHP process‘ high overall efficiency. The PEFof the DHN can thus be determined according to;fDHifF , i EF P QDHfEl .As producti<strong>on</strong> of products other than electricity is notdefined in EN 15316-4-5 the power b<strong>on</strong>us method hasbeen extended by regarding the produced pyrolysisslurry as a ―b<strong>on</strong>us‖ as well. The PEF of the pyrolysisintegrated CHP plant is thus calculated as:fDH fF , i EF, i P fEl .iQDH EPyro fPyroPrimary Energy FactorThe total primary energy factor is the sum of all PE inputto the energy system divided by the useful energydelivered at the system border. It thus describes howmuch PE input is needed in order to obtain <strong>on</strong>e unit ofenergy used <strong>and</strong> can hence be seen as an invertedefficiency.In st<strong>and</strong>ard EN 15316-4-5 [3] more detailed guidelinesfor the calculati<strong>on</strong> of PEFs of DH systems are defined.According to EN 15316-4-5 PEFs can be calculated fora certain part of the energy system. In this study thesystem boundary comprises the power plants <strong>and</strong> theDHN.The PEF of the DHN has been calculated applying thepower b<strong>on</strong>us method. If yearly dem<strong>and</strong> data of the DHN<strong>and</strong> the generati<strong>on</strong> data are known, the PEF of the DHNcan be calculated by applying the so-called powerb<strong>on</strong>us method. The power-b<strong>on</strong>us method is derivedfrom the energy balance of the building which can bewritten as: fF , i EF fDHQDH PfEl .,iwhere E F , Q DH <strong>and</strong> P are the heat of the fuels used, DH<strong>and</strong> power co-generated respectively. f F,i , f DH <strong>and</strong> f El. arethe PEFs of the fuels used, the DHN <strong>and</strong> of the cogeneratedpower.172In this study PEFs as shown in table 2 have been used:Table 2: Primary energy factors <strong>and</strong> CO 2 emissi<strong>on</strong>coefficients for fuels <strong>and</strong> productsf BM2f Oil2f El.1f Pyro11.09 c CO2/BM21.35 c CO2/Oil23.11 c CO2/El.11.28 c CO2/Pyro1kg/MWh143302701 : value is calculated, 2 : value is taken from EN 15603, Annex EFuels assumed to be used are wood logs for the CHPplant <strong>and</strong> fuel oil for the heat-<strong>on</strong>ly/backup boiler(s) <strong>and</strong>their PEFs are taken form annex E of EN 15603. ThePEF of electricity producti<strong>on</strong> in Finl<strong>and</strong> has beenderived from [10]. The PEF of pyrolysis slurry in ast<strong>and</strong>-al<strong>on</strong>e unit has been calculated assuming a fluegas dryer (which is c<strong>on</strong>sidered as the drying technologymost likely to be applied) with an energy c<strong>on</strong>sumpti<strong>on</strong> of3300 kJ/kg water evaporated [9] <strong>and</strong> a heat of pyrolysisof 1.87 kJ/kg [7]. Although the st<strong>and</strong>ard asks for moredetailed analysis of the energy chain as e.g.c<strong>on</strong>siderati<strong>on</strong> of transport, transmissi<strong>on</strong> <strong>and</strong> otherprocessing should be included, this has not beenimplemented into this study since those factors areassumed not to differ between integrated <strong>and</strong> separatedproducti<strong>on</strong> of pyrolysis oil.14
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In addition, it can also be observe
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