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>iaCO 2 Emissi<strong>on</strong> CoefficientThe CO 2 rating is d<strong>on</strong>e by calculating CO 2 emissi<strong>on</strong>coefficients (c CO2 ) that quantify the total amount of fossilfuel derived CO 2 , emitted to the atmosphere, per unitdelivered energy. As for the primary energy factor thesystem boundary comprises of power plants <strong>and</strong> DHN.Also the power b<strong>on</strong>us method is applied for calculatingthe DHN‘s specific CO 2 emissi<strong>on</strong>s. For the sake ofcompleteness it must be menti<strong>on</strong>ed that CO 2 -equivalentemissi<strong>on</strong>s of other greenhouse gases can opti<strong>on</strong>ally beincluded. However this has not been implemented intothis study, due to a lack of data. Similarly to the PEF theCO 2 emissi<strong>on</strong> coefficients for the base case arecalculated as:cCO2, DHiEF , icCO2, F , iQDHAnd for the modified plant as:cCO2, DHiEF , i cCO2, F , i P c P cQCO2, El .CO2, El .DH. EPyro cCO2, PyroE F,i , E Pyro , P <strong>and</strong> Q DH represent heat in fuels, heat inpyrolysis slurry <strong>and</strong> co-generated electricity <strong>and</strong> DHrespectively. Accordingly, c CO2,F,i , c CO2,Pyro , c CO2,El. <strong>and</strong>c CO2,DH are the related CO 2 emissi<strong>on</strong> coefficients. Thecorresp<strong>on</strong>ding values are given in table 2.RESULTSIn table 3, three simulati<strong>on</strong> cases are presented: thebase case (case 1), pyrolysis integrati<strong>on</strong> with the sameoperati<strong>on</strong> hours (case 2) <strong>and</strong> the maximum pyrolysisslurry producti<strong>on</strong> (case 3) with prol<strong>on</strong>ged operati<strong>on</strong>.hours <strong>and</strong> a DH load as low as 30% (matching 18% ofthe total DH load). It can be seen from the table that forall cases the DH output is the same for the 100-50%operating points. This results, in the first two cases, inan identical total DH output of 70.85 GWh. Thiscorresp<strong>on</strong>ds with 75% of the total yearly DH load. Dueto steam extracted to the dryer, the enthalpy flowthrough the turbine in part load is decreased, whichresults in a lower electricity producti<strong>on</strong> in part load forthe cases 2 <strong>and</strong> 3. Already for the sec<strong>on</strong>d casepyrolysis slurry with an energy c<strong>on</strong>tent in the samerange as the DH load can be produced. Fuel input,which is defined as wood burned in the boiler <strong>and</strong> woodentering the dryer for subsequent pyrolysis, increaseswith falling load for load levels 60% <strong>and</strong> higher. In thosecases the boiler combusti<strong>on</strong> power is 100%, but it isdecreased for lower load levels as explained above. Ifoperati<strong>on</strong> hours are extended by supplying lower DHloads with the CHP plant (case 3), total pyrolysis slurryproducti<strong>on</strong> can be increased by approximately 55%,electricity producti<strong>on</strong> by 7.8% compared to the basecase. Further DH producti<strong>on</strong> is increased byapproximately 14.7%, covering now 86% of the total DHdem<strong>and</strong>. This directly decreases the fossil fuelledbackup power as shown in table 4. The needed backupheat is almost cut in half. Together with the additi<strong>on</strong>allyproduced electricity this substantially improves theprimary energy factor to 0.68 which certainly will have apositive influence <strong>on</strong> the PEF of the buildings c<strong>on</strong>nectedto the DHN. For case 2 the improvement is marginal.The CO 2 emissi<strong>on</strong> coefficient changes somewhatc<strong>on</strong>troversially by increasing in the 2 nd case. This isbecause the loss in electricity b<strong>on</strong>us cannot becompensated by the produced pyrolysis slurry, since theCO 2 emissi<strong>on</strong> coefficients differ widely. However forcase 3 specific CO 2 emissi<strong>on</strong>s become even negative.The negative value is very unlikely to reach <strong>and</strong> can beexplained with the not fully accounted fuel producti<strong>on</strong>chain. Nevertheless, it is obvious that the DHN‘s CO 2emissi<strong>on</strong> factors can be c<strong>on</strong>siderably reduced with thepresented integrati<strong>on</strong> c<strong>on</strong>cept.173
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>iaTable 3: Results – Multiperiod ModelBase Case - Case 1CHP DH Load [%] 100 90 80 70 60 50 40 30 totalTime [h] 2440 530 530 530 530 530 - - 212 daysFuel Input [MW] 25.90 23.19 20.39 17.47 14.58 11.91 - - 109.56 GWhPower [MW] 6.29 5.64 4.91 4.06 3.22 2.54 - - 26.13 GWh<strong>District</strong> Heat [MW] 16.50 14.85 13.20 11.55 9.90 8.25 - - 70.85 GWhCHP + Pyrolysis - Case 2CHP DH Load [%] 100 90 80 70 60 50 40 30 totalTime [h] 2440 530 530 530 530 530 - - 212 daysFuel Input [MW] 25.90 36.49 44.24 52.42 60.21 53.88 - - 194.13 GWhPower [MW] 6.29 5.54 4.69 3.71 2.88 2.25 - - 25.45 GWh<strong>District</strong> Heat [MW] 16.50 14.85 13.20 11.55 9.90 8.25 - - 70.85 GWhPyrolysis Slurry [MW] 12.21 21.16 30.60 39.58 36.76 - - 74.31 GWhCHP + Pyrolysis - Prol<strong>on</strong>ged Operati<strong>on</strong> Hours - Case 3CHP DH Load [%] 100 90 80 70 60 50 40 30 totalTime [h] 2266 633 633 633 633 633 633 633 279 daysFuel Input [MW] 25.90 36.49 44.24 52.42 60.21 50.97 39.56 28.88 256.62 GWhPower [MW] 6.29 5.54 4.69 3.71 2.88 2.27 1.71 1.18 28.17 GWh<strong>District</strong> Heat [MW] 16.50 14.85 13.20 11.55 9.90 8.25 6.60 4.95 81.26 GWhPyrolysis Slurry [MW] 0.00 12.21 21.16 30.60 39.58 33.79 26.11 19.00 115.46 GWhTable 4: Results - PEF <strong>and</strong> CO2 CoefficientBase CaseCase 1CHP + PyrolysisCase2CHP + Pyrolysis -Prol<strong>on</strong>ged Operati<strong>on</strong>Case 3Required Backup Power MWh 27.8 27.8 15.5Total PEF [-] 0.80 0.79 0.68CO2 Coefficient kg/MWh 38.6 42.1 -5.3CONCLUSION AND DISCUSSIONThe work shows that by integrati<strong>on</strong> of a CHP plant withwood pyrolysis operati<strong>on</strong> hours can be increases by30%, a valuable product can be co-produced <strong>and</strong> PEEas well as the CO 2 emissi<strong>on</strong> coefficient of the DHN canbe substantially improved. As next steps morecomprehensive data of the fuel supply chain should beimplemented to get more realistic values that willapprove the trend shown with this work. The processcan be further improved by integrating heat that is setfree during the c<strong>on</strong>densati<strong>on</strong> of the pyrolysis liquid <strong>and</strong>gaseous product. The heat is available in atemperature range from approximately 500 °C to 25 °C<strong>and</strong> could hence be used for steam superheating,feedwater preheating, but also for DH generati<strong>on</strong>. Thisintegrati<strong>on</strong> is not a simple task since many plantparameters influence each other. The heat integrati<strong>on</strong>must be carried out together with a pinch analysis toassure an energy efficient integrati<strong>on</strong>.174Another open questi<strong>on</strong> is the influence of the realpyrolysis gas <strong>on</strong> the combusti<strong>on</strong> temperature <strong>and</strong> fluegas properties. In order to gather more details of thepyrolysis process a simple pyrolysis model is currentlyunder development. Together with the power plantmodel the integrati<strong>on</strong> can be further optimised aimingfor highest PEE al<strong>on</strong>g with low CO 2 emissi<strong>on</strong>coefficients.Further an ec<strong>on</strong>omic analysis should be carried out inorder to show potential ec<strong>on</strong>omic benefits. Theintegrati<strong>on</strong> itself seems to be viable – a statement thatis supported by a press release from June 2009 whereboiler manufacturer Metso <strong>and</strong> forestry company UPMannounced the development of a new viable fastpyrolysis process benefitting from the integrati<strong>on</strong> with aCHP plant [11].C<strong>on</strong>cerning the European st<strong>and</strong>ards used forevaluati<strong>on</strong>, it can be said that the power b<strong>on</strong>us methodcan be easily adapted to a polygenerati<strong>on</strong> c<strong>on</strong>cept
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