EXPERIMENTS AND NUMERICAL MODELING OF...

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EXPERIMENTS AND NUMERICAL MODELING OF MEAT AND BONE MEAL PYROLYSIS IN A ROTARY KILN Pawel ZIÓLKOWSKI * Marcin KANTOREK Keywords: Pyrolysis; Meat and bone meal; Numerical modeling Abstract: The paper presents aspects of modelling the pyroly- sis of meat and bone meal (MBM) in a rotary kiln. The pyrolysis of MBM produces a solid fraction which can be used as a fuel, a liquid fraction with potential chemical applications and a low heating value gas. The meat and bone meal pyrolysis was carried out at the temperature of 900 o C. Main features of experiments and numerical model of the pyrolysis were described. The model was validated by comparing the calculated values to measure- ment. The results of numerical model agree well with the exper- imental data. The numerical calculations have been carried out in the CFM (Computational Flow Mechanics ) code. 1. Introduction Meat and bone meal produced in animal slaughterhouses and farms, becomes nowa- days an important waste (Becker, Ferrante, Briens, Berruti & Cascarosa 2011). Since the Bovine Spongiform Encephalopathy (BSE) crisis, the addition of MBM as pro- tein rich product into the cattle feed has been restricted (European Commission De- cision94/381/ECof June 1994 concerning certain protection measures with regard to bovine spongiform encephalopathy and the feeding ofmammalian derived protein 1994). Therefore, approximately 3 million tons per year of MBM, that requires an envi- ronmental friendly and safe management method, are produced in Europe (Becker et al. 2011). Contemporary methods of handling MBM is by burning it in cement kilns or depositing in landfills. However, MBM could be converted in pyrolysis, which would be safe and environmentally friendly (Becker et al. 2011, Kantorek, Kozakiewicz, Folga & Karcz 2009, Butmankiewicz, Modliński, Kantorek & Rzepa 2007). Many studies have been carried out on the pyrolysis. For example the pyrolysis of MBM has been studied in fixed bed (Ayllón, Aznar, S´ anchez, Gea & Arauzo 2006), thermobalance reactors (Conesa, Font, Fullana, Mart´ ın-Gullón, Aracil, G´ alvez, Moltó & Gómez- * The Szewalski Institute of Fluid-Flow Machinery Polish Academy of Sciences, Energy Conversion Department Wroclaw University of Technology, Mechanical and Power Engineering

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Page 1: EXPERIMENTS AND NUMERICAL MODELING OF …sdpg.pg.gda.pl/pij/files/2012/...P.-Kantorek-M.-Modeling-of-meat.pdfEXPERIMENTS AND NUMERICAL MODELING OF MEAT AND BONE MEAL PYROLYSIS IN A

EXPERIMENTS AND NUMERICALMODELING OF MEAT AND BONE MEAL

PYROLYSIS IN A ROTARY KILN

Paweł ZIÓŁKOWSKI∗ Marcin KANTOREK†

Keywords: Pyrolysis; Meat and bone meal; Numericalmodeling

Abstract: The paper presents aspects of modelling the pyroly-sis of meat and bone meal (MBM) in a rotary kiln. The pyrolysisof MBM produces a solid fraction which can be used as a fuel,a liquid fraction with potential chemical applications and a lowheating value gas. The meat and bone meal pyrolysis was carriedout at the temperature of 900oC. Main features of experimentsand numerical model of the pyrolysis were described. The modelwas validated by comparing the calculated values to measure-ment. The results of numerical model agree well with the exper-imental data. The numerical calculations have been carried outin the CFM (Computational Flow Mechanics) code.

1. Introduction

Meat and bone meal produced in animal slaughterhouses and farms, becomes nowa-days an important waste (Becker, Ferrante, Briens, Berruti & Cascarosa 2011). Sincethe Bovine Spongiform Encephalopathy (BSE) crisis, the addition of MBM as pro-tein rich product into the cattle feed has been restricted (European Commission De-cision94/381/ECof June 1994 concerning certain protection measures with regard tobovine spongiform encephalopathy and the feeding ofmammalian derived protein 1994).Therefore, approximately 3 million tons per year of MBM, that requires an envi-ronmental friendly and safe management method, are produced in Europe (Beckeret al. 2011). Contemporary methods of handling MBM is by burning it in cement kilnsor depositing in landfills. However, MBM could be converted in pyrolysis, which wouldbe safe and environmentally friendly (Becker et al. 2011, Kantorek, Kozakiewicz, Folga& Karcz 2009, Butmankiewicz, Modliński, Kantorek & Rzepa 2007). Many studieshave been carried out on the pyrolysis. For example the pyrolysis of MBM has beenstudied in fixed bed (Ayllón, Aznar, Sanchez, Gea & Arauzo 2006), thermobalancereactors (Conesa, Font, Fullana, Martın-Gullón, Aracil, Galvez, Moltó & Gómez-

∗The Szewalski Institute of Fluid-Flow Machinery Polish Academy of Sciences, Energy ConversionDepartment†Wroclaw University of Technology, Mechanical and Power Engineering

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Rico 2009, Skodras, Grammelis & Basinas 2007, Skodras & Sakellaropoulos 2002)and a mechanically fluidized reactor (Becker et al. 2011).

The purpose of this work is to analyze pyrolysis of MBM in rotary kiln and com-pare experimental results with numerical simulation. The numerical analysis wasperformed with use of CFM codes.

2. Experimental part

The experimental research was conducted in a pilot installation presented in Fig. 1.This installation includes the rotary kiln, the fluidized bed, the exit chamber, theinflame burner, the burner, the fan, the fuel tank, the system of inflame burner,the system of burner and the outlet of exhaust. The most important parts of theinstallation are the rotary kiln and the fluidized bed. The pyrolysis proceeds in therotary kiln which is a heat-resistant concrete cylinder of 1.5 m diameter with aninternal height of 8 m. Next, in the fluidized bed happens combustion of char andpyrolytic gases. Released exhaust gases are directed to heat recovery steam generator.

Subjected to research was the sole pyrolysis process, while the experimental dataare considered only for the exhaust zone of the rotary kiln. The measured quantitieswere the temperature, pressure and pyrolysis gas composition. The results of theexperiment are presented in Table 1, 2 and 3.

Fig. 1. Flow sheet of the experimental set-up (1 - rotary kiln, 2 - exit chamber,3 - fluidized bed, 4 - inflame burner, 5 - burner, 6 - fan, 7 - fuel tank,8 - system of inflame burner, 9 -system of burner, 10 - outlet of exhaust).

3. Numerical model

Mathematical models in CFM employ mass and energy balance equations in the inte-grated form (also called 0D or engineering form) (Badur 2003, Ziółkowski, Lemański,

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Badur & Zakrzewski 2012). In this section computational procedures of the pyroly-sis in a rotary kiln is presented. Computation of the rotary kiln requires an energybalance to be performer including all input and output energy fluxes. Heat losses inthe combustion chamber (into the surrounding) are specified with use of the rotarykiln efficiency ηRK . Chemical energy of the charge (MBM) is defined to be (Topolski,Lemański & Badur 2003, Badur 2005):

QMBM = mMBM ·WMBM , (1)

where: mMBM - meat and bone meal mass flux [ kg/s]; a WMBM - meat and bonemeal calorific value [kJ/kg].

Energy balance for the rotary kiln may be expressed as (Topolski et al. 2003,Badur 2005):

ηRK · QMBM + mMBM · hMBM = mG · hG + QG + mA · hA + mC · hC + QC . (2)

where: mG- gaseous phase mass flux [kg/s], mA- mass flux of ash [kg/s],hMBM – MBM enthalpy [kJ/kg], hG– gaseous phase enthalpy [kJ/kg], hA– ash en-thalpy [kJ/kg], QG- chemical energy of the gaseous phase [kW] and QC - chemicalenergy of the char [kW].

Additionally, chemical energy of the gaseous phase is defined to be:

QG = mG ·WG, (3)

where: WG- the gaseous phase calorific value [kJ/kg].Chemical energy of the char may be expressed as:

QC = mC ·WC , (4)

where: WC- the char calorific value [kJ/kg].Moreover, it requires mentioning, that the following mass balances need to be

satisfied:mMBM = mG + mA + mC . (5)

4. Results

The proximate analysis (see Table 1) shows that the charge contains a high amountof volatile matter (67,34%), and other components like: moisture (14,6%), ash (4,4%)and char (13,66%). In turn ultimate analysis of meat and bone meal was presentedin Table 2. The proximate and ultimate analysis of MBM provides the boundaryconditions for numerical model. Additionally boundary conditions are temperature,pressure and mass flux of the substratum.

The main products from the MBM pyrolysis in the rotary kiln were the gasesphase, the ash and the char (see Table 3). Also, composition of the product was in-troduced. The result of numerical calculation is temperature. The difference betweentemperatures is only 7 K, so results of numerical model describe well the experimentaldata.

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Tab. 1. Proximate analysis of MBM.

Parameter Unit Experimental ModelMoisture % w/w 14.60 14.60Volatiles % w/w 67.34 67.34

Ash % w/w 4.40 4.40Char % w/w 13.66 13.66

Tab. 2. Ultimate analysis of MBM.

Parameter Unit Experimental ModelAsh % w/w 5.21 5.21

Carbon % w/w 53.23 53.23Hydrogen % w/w 9.99 9.99Nitrogen % w/w 8.67 8.67Sulphur % w/w 0.32 0.32Oxygen % w/w 22.33 22.33Chlorine % w/w 0.24 0.24

Tab. 3. Parameters after pyrolysis.

Parameter Unit Experimental ModelChar % w/w 3.29 3.29Ash % w/w 12.66 12.66H2O % w/w 31.84 31.84CO2 % w/w 4.23 4.23CO % w/w 5.48 5.48H2 % w/w 30.18 30.18H2S % w/w 0.11 0.11N2 % w/w 3.45 3.45

C2H2 % w/w 1.04 1.04C2H4 % w/w 1.57 1.57C2H6 % w/w 0.94 0.94CH4 % w/w 2.87 2.87C3H8 % w/w 2.34 2.34

Temperature oC 900 907Pressure Pa 101210 101210Mass flux ton/hr 1 1

5. Conclusions

The present work consist of experimental and numerical results of charge. In orderto validate the model, specific measurements of the MBM were made on inlet semi-

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industrial rotary kiln, and the solid and gas composition were determined by analizingsamples taken at the outlet area of rotary kiln. The agreement between these mea-surement and the results of the calculations is satisfactory and confirms the validityof the model.

The numerical model results agree well with the experimental data. Correct resultvalidation allows for model employment to introductory prognostics of the main pa-rameters in fast pyrolysis during animal waste utilisation. The numerical calculationshave been carried out in the CFM (Computational Flow Mechanics) code and showvery good prospects.

References

Ayllón, M., M. Aznar, J. L. Sanchez, G. Gea & J. Arauzo (2006), ‘Infuence of tem-peratureand heating rate on the fixed bed pyrolysis of meat and bone meal’,Chemical Engineering Journal pp. 85–96.

Badur, J. (2003), Numeryczne modelowanie zrównoważonego spalania w turbinachgazowych, IMP PAN, Gdańsk.

Badur, J. (2005), Pięć wykładów ze współczesnej termomechaniki płynów, ZakładKonwersji Energii IMP PAN, Gdańsk.

Becker, E. J., L. Ferrante, C. Briens, F. Berruti & J. Arauzo Cascarosa (2011), ‘Pyrol-ysis of meat-meal and bone-meal blends in mechanically fluidized reacto’, Journalof Analytical and Applied Pyrolysis pp. 359–367.

Butmankiewicz, H. T., Z. Modliński, M. Kantorek & K. Rzepa (2007), ‘Urzadzeniedo wytwarzania energii cieplnej’. Opis patentowy 210758.

Conesa, J. A., R. Font, A. Fullana, I. Martın-Gullón, I. Aracil, A. Galvez, J. Moltó &M.F. Gómez-Rico (2009), ‘Comparison between emissions from the pyrolysis andcombustion of different wastes’, Journal of Analytical Applied Pyrolysis pp. 95–102.

European Commission Decision94/381/ECof June 1994 concerning certain protec-tion measures with regard to bovine spongiform encephalopathy and the feedingofmammalian derived protein (1994). L 172, 07/07/1994.

Kantorek, H. M., A. Kozakiewicz, K. Folga & M. Grabowicz Karcz (2009), ‘Możli-wości wykorzystania mączki mięsno–kostnej, jako paliwa w instalacjach energety-cznych’, Energetyka i Ekologia pp. 40–47.

Skodras, G. & G.P. Sakellaropoulos (2002), ‘Mineral matter effects in lignite gasifica-tion’, Fuel Processing Technology pp. 151–158.

Skodras, G., P. Grammelis & P. Basinas (2007), ‘Pyrolysis and combustion behaviourof coal-mbm blends’, Bioresource Technology pp. 1–8.

Topolski, J., M. Lemański & J. Badur (2003), Model matematyczny wysokotemper-aturowego ogniwa paliwowego sofc w kodzie com-gas.

Ziółkowski, P., M. Lemański, J. Badur & L. Nastałek (2012), ‘Power augmentation ofPGE Gorzów gas turbine by steam injection – Thermodynamic overwiev’, RynekEnergii pp. 161–167.

Ziółkowski, P., M. Lemański, J. Badur & W. Zakrzewski (2012), ‘Wzrost sprawnościturbiny gazowej przez zastosowanie idei Szewalskiego’, Rynek Energii pp. 63–70.