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Frontiers of Chemical Science and Engineering

ISSN 2095-0179

ISSN 2095-0187(Online)

CN 11-5981/TQ

邮发代号 80-969

2019 Impact Factor: 3.552

Frontiers of Chemical Science and Engineering  2018, Vol. 12 Issue (4): 660-669   https://doi.org/10.1007/s11705-018-1773-0
  本期目录
Proposed EU legislation to force changes in sewage sludge disposal: A case study
Vojtěch Turek(), Bohuslav Kilkovský, Zdeněk Jegla, Petr Stehlík
Institute of Process Engineering, Faculty of Mechanical Engineering, Brno University of Technology, 61669 Brno, Czech Republic
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Abstract

The consequences of changes planned in the European Union legislation relevant to the disposal of sewage sludges are discussed. A specific municipal waste water treatment plant is analyzed in terms of drying and subsequent combustion or pyrolysis of the produced stabilized sludge, and the respective net energy balances are carried out. A simplified economic analysis of the two disposal options is presented, which suggest that combustion of the sludge would be economically infeasible while pyrolysis of the sludge in a modular, self-sufficient container unit can bring a small financial benefit due to the selling of the produced phosphorus-rich biochar.

Key wordssewage sludge    drying    combustion    pyrolysis
收稿日期: 2018-02-22      出版日期: 2019-01-03
Corresponding Author(s): Vojtěch Turek   
 引用本文:   
. [J]. Frontiers of Chemical Science and Engineering, 2018, 12(4): 660-669.
Vojtěch Turek, Bohuslav Kilkovský, Zdeněk Jegla, Petr Stehlík. Proposed EU legislation to force changes in sewage sludge disposal: A case study. Front. Chem. Sci. Eng., 2018, 12(4): 660-669.
 链接本文:  
https://academic.hep.com.cn/fcse/CN/10.1007/s11705-018-1773-0
https://academic.hep.com.cn/fcse/CN/Y2018/V12/I4/660
Fig.1  
Fig.2  
Sludge Daily production/kg Dry matter/wt-% Organic matter (dry basis)/wt-%
Mixed 70700 3.88 72.50
Stabilized 69602 2.36 54.15
Dewatered 8055 19.50 51.70
Tab.1  
Daily production Note
Biogas 1114 Nm3 Methane: 61.7 mol-%,LHV: 22.13 MJ·Nm–3
Heat 13070 MJ CHP heat efficiency: 53%
Power 2330 kWh (8380 MJ) CHP power efficiency: 34%
Tab.2  
Fig.3  
Dewatered Dried
Dry matter 19.50 wt-% 90.00 wt-%
Organic matter (dry basis) 51.70 wt-%
Mass flow rate 8055 kg·d–1 1745 kg·d–1
Heat required for drying 18641 MJ·d–1
Tab.3  
Parameter Value
Lower heating value (measured):
?????????Organic matter 19.1 MJ·kg–1
?????????Dried sludge 8.89 MJ·kg–1
Specific heat capacity of dry matter (measured) 1.231 kJ·kg–1
Combustion air required 5.05 kg·(kg dry matter)–1
Thermal energy:
????????Obtainable from combustion of the organic matter 15510 MJ·d–1
????????Required to sustain combustion (at 80% combustion efficiency) 12035 MJ·d–1
Net thermal energy gain 3475 MJ·d–1
Tab.4  
Fig.4  
Fig.5  
Fig.6  
Value Notes/reference
Dryer
Thermal energy demand for drying 18641 MJ·d–1 See Table 3
Investment cost 591500 € From the technology supplier
Operating cost including maintenance and personnel 85080 €·y–1
Scenario 2: Biogas production & combustion of the dried digestate
Incinerator investment cost 6605000 € Ashwekar et al. [43]
Total investment cost incl. dryer 7196500 €
Incinerator operating cost incl. maintenance and personnel 1317700 €·y–1 Ashwekar et al. [43]
Total operating cost incl. dryer 1402780 €·y–1
Landfilling of ash incl. transport 8700 €·y–1 From a landfill operator
Profits
Net balance excl. investment cost –1411480 €·y–1
Scenario 3: Biogas production & pyrolysis of the dried digestate
PYREG investment cost 820000 € From the technology supplier
Total investment cost incl. dryer 1411500 €
PYREG operating cost incl. maintenance and personnel 18590 €·y–1 From the technology supplier
Total operating cost incl. dryer 103670 €·y–1
Other associated costs
Profit from selling biochar at 500 EUR·t–1 113740 €·y–1 Sundberg [44]
Net balance excl. investment cost 10070 €·y–1
Tab.5  
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