Skip to main content

Advertisement

Log in

Modeling for waste management associated with environmental-impact abatement under uncertainty

  • Research Article
  • Published:
Environmental Science and Pollution Research Aims and scope Submit manuscript

Abstract

Municipal solid waste (MSW) treatment can generate significant amounts of pollutants, and thus pose a risk on human health. Besides, in MSW management, various uncertainties exist in the related costs, impact factors, and objectives, which can affect the optimization processes and the decision schemes generated. In this study, a life cycle assessment-based interval-parameter programming (LCA-IPP) method is developed for MSW management associated with environmental-impact abatement under uncertainty. The LCA-IPP can effectively examine the environmental consequences based on a number of environmental impact categories (i.e., greenhouse gas equivalent, acid gas emissions, and respiratory inorganics), through analyzing each life cycle stage and/or major contributing process related to various MSW management activities. It can also tackle uncertainties existed in the related costs, impact factors, and objectives and expressed as interval numbers. Then, the LCA-IPP method is applied to MSW management for the City of Beijing, the capital of China, where energy consumptions and six environmental parameters [i.e., CO2, CO, CH4, NOX, SO2, inhalable particle (PM10)] are used as systematic tool to quantify environmental releases in entire life cycle stage of waste collection, transportation, treatment, and disposal of. Results associated with system cost, environmental impact, and the related policy implication are generated and analyzed. Results can help identify desired alternatives for managing MSW flows, which has advantages in providing compromised schemes under an integrated consideration of economic efficiency and environmental impact under uncertainty.

This is a preview of subscription content, log in via an institution to check access.

Access this article

Price excludes VAT (USA)
Tax calculation will be finalised during checkout.

Instant access to the full article PDF.

Institutional subscriptions

Fig. 1
Fig. 2
Fig. 3
Fig. 4
Fig. 5
Fig. 6
Fig. 7
Fig. 8

Similar content being viewed by others

Abbreviations

f ± :

The net system cost ($)

t :

Index for transfer station, t = 1, 2, … 6

i :

Index for incinerator, i = 1, 2, … 6

c :

Index for composting, c = 1, 2, … 9

X ± utk :

Solid waste stream from the urban districts to transfer station t during period k (tonne/day)

X ± uik :

Solid waste stream from the urban districts to incinerator facility i during period k (tonne/day)

X ± ulk :

Solid waste stream from the urban districts to landfill l during period k (tonne/day)

X ± tik :

Solid waste stream from transfer station t to incinerator facility i during period k (tonne/day)

X ± clk :

Solid waste stream from composting facility c to landfill l during period k (tonne/day)

D ± uc :

The distance between urban district and composting facility c (km)

D ± ul :

The distance between urban district and landfill l (km)

D ± ti :

The distance between transfer station t and incinerator facility i (km)

D ± cl :

The distance between composting facility c and landfill l (km)

F ± :

Consumption of fuel oil for transporting 1 tonne of solid waste per kilometer (l/km tonne)

EL ± :

Consumption of electricity for disposing 1 tonne of solid waste (kwh/tonne)

TD ± tk :

Consumption of diesel for disposing 1 tonne of solid waste in transfer station t (l / tonne)

TI ± ik :

Consumption of diesel for disposing 1 tonne of solid waste in incinerator facility i (l/tonne)

\( O{P}_{{}_{ck}}^{\pm } \) :

Operating costs of composting facility c during time period k ($/tonne)

\( O{P}_{{}_{lk}}^{\pm } \) :

Operating costs of landfill l during time period k ($/tonne)

\( {P}_{{}_z}^{\pm } \) :

Unit price of recycled material z ($/tonne)

FE ± ik :

Residue flow rate from incinerator facility i to landfill l (%)

RE ± ik :

Revenues of unit MSW disposed by the incinerator facility i during time period k ($/tonne)

ER md :

Emission rate of the mth kind of the pollutant gas for 1 kg fuel oil (kg/l)

EO ± mc :

Emission rate of the mth kind of the pollutant gas for 1 tonne MSW in composting facility c (kg/tonne)

EO ± ml :

Emission rate of the mth kind of the pollutant gas for 1 tonne MSW in landfill l (kg/tonne)

δ ± l :

The capacity rate of landfill l for urban district (% of the whole capacity)

l :

Index for landfill, l = 1, 2, … 16

k :

Planning period, k = 1, 2, 3

lk :

The length of period k

z :

Recycling material, z = 1, metal; z = 2, paper; z = 3, plastic; z = 4, glass

X ± uck :

Solid waste stream from the urban districts to composting facility c during period k (tonne/day)

X ± tck :

Solid waste stream from transfer station t to composting facility c during period k (tonne/day)

X ± tlk :

Solid waste stream from transfer station t to landfill l during period k (tonne/day)

X ± ilk :

Solid waste stream from incinerator facility i to landfill l during period k (tonne/day)

\( {D}_{{}_{ut}}^{\pm } \) :

The distance between urban district and transfer station t (km)

D ± ui :

The distance between urban district and incinerator facility i (km)

D ± tc :

The distance between transfer station t and composting facility c (km)

D ± tl :

The distance between transfer station t and landfill l (km)

D ± il :

The distance between incinerator facility i and landfill l (km)

P ± F :

Unit price of fuel oil ($/l)

ColC ± k :

Collection cost during period k ($/t)

\( {P}_{{}_{EL}}^{\pm } \) :

Unit price of electricity ($/kwh)

CE ± k :

Dissipation coefficient of electricity for the incinerator facility (%)

TC ± ck :

Consumption of diesel for disposing 1 tonne of solid waste in composting facility c (l/tonne)

TL ± lk :

Consumption of diesel for disposing 1 tonne of solid waste in landfill l (l/tonne)

\( O{P}_{{}_{tk}}^{\pm } \) :

Operating costs of transfer station t during time period k ($/tonne)

\( O{P}_{{}_{ik}}^{\pm } \) :

Operating costs of incinerator i during time period k ($/tonne)

RC zt :

Recovery rate of material z in transfer station t (%)

FE ± ck :

Residue flow rate from composting facility c to landfill l (%)

RE ± ck :

Revenues of unit MSW disposed by the composting facility c during time period k ($/tonne)

EO ± mt :

Emission rate of the mth kind of the pollutant gas for 1 tonne MSW in transfer station t (kg/tonne)

EO ± mi :

Emission rate of the mth kind of the pollutant gas for 1 tonne MSW in incinerator facility i (kg/tonne)

PE m :

Unit price for purchasing the mth kind of the pollutant gases credit or disposing the mth kind of the pollutant gases

References

  • Antonopoulos IS, Karagiannidis A, Tsatsarelis T, Perkoulidis G (2013) Applying waste management scenarios in the Peloponnese region in Greece: a critical analysis in the frame of life cycle assessment. Environ Sci Pollut Res 20:2499–2511

    Article  CAS  Google Scholar 

  • Arena U, Mastellone ML, Perugini F (2003) The environmental performance of alternative solid waste management options: a life cycle assessment study. Chem Eng J 96:207–222

    Article  CAS  Google Scholar 

  • Banar M, Cokaygil Z, Ozkan A (2009) Life cycle assessment of solid waste management options for Eskisehir, Turkey. Waste Manag 29:54–62

    Article  Google Scholar 

  • Beijing Municipal Bureau of Statistics (2010) Beijing statistical yearbook. China Statistics Press, Beijing (In Chinese)

    Google Scholar 

  • Beijing Municipal Solid Waste Management (2010) Available at http://www.solidwaste.com.cn/report/beijinglaji20060419/2010sheshi.htm (In Chinese)

  • Beijing Municipal Solid Waste Management (2012) Available at http://www.solidwaste.com.cn/report/beijinglaji20060419/2012sheshi.htm (In Chinese)

  • BMAC (2011) Beijing environmental sanitation development report. Beijing Municipal Administration Commission (In Chinese)

  • Buttol P, Masoni P, Bonoli A, Goldoni S, Belladonna V, Cavazzuti C (2007) LCA of integrated MSW management systems: case study of the Bologna District. Waste Manag 27:1059–1070

    Article  CAS  Google Scholar 

  • Chen TC, Lin CF (2008) Greenhouse gases emissions from waste management practices using life cycle inventory model. J Hazard Mater 155:23–31

    Article  CAS  Google Scholar 

  • Chen WT, Li YP, Huang GH, Chen X, Li YF (2010) A two-stage inexact-stochastic programming model for planning carbon dioxide emission trading under uncertainty. Appl Energy 87:1033–1047

    Article  CAS  Google Scholar 

  • Cleary J (2009) Life cycle assessments of municipal solid waste management systems: a comparative analysis of selected peer-reviewed literature. Environ Int 35:1256–1266

    Article  Google Scholar 

  • Cui L, Chen LR, Li YP, Huang GH, Li W, Xie YL (2011) An interval-based regret-analysis method for identifying long-term municipal solid waste management policy under uncertainty. J Environ Manage 92:1484–1494

    Article  CAS  Google Scholar 

  • Curran MA (2004) The status of life-cycle assessment as an environmental management tool. Environ Prog 23:277–283

    Article  CAS  Google Scholar 

  • Dai C, Li YP, Huang GH (2011) A two-stage support-vector-regression optimization model for municipal solid waste management—a case study of Beijing, China. J Environ Manage 92:3023–3037

    Article  CAS  Google Scholar 

  • Davila E, Chang NB (2005) Landfill space consumption dynamics in the Lower Rio Grande Valley by grey integer programming-based games. J Environ Manage 75:353–365

    Article  Google Scholar 

  • Davila E, Chang NB (2008) Municipal solid waste characterizations and management strategies for the Lower Rio Grande Valley, Texas. Waste Manag 28:776–794

    Article  Google Scholar 

  • Dong J, Ni MJ, Chi Y, Zou DA, Fu C (2013) Life cycle and economic assessment of source-separated MSW collection with regard to greenhouse gas emissions: a case study in China. Environ Sci Pollut Res 20:5512–5524

    Article  CAS  Google Scholar 

  • Feo GD, Malvano C (2009) The use of LCA in selecting the best MSW management system. Waste Manag 29:1901–1915

    Article  Google Scholar 

  • Gunamantha M, Sarto (2012) Life cycle assessment of municipal solid waste treatment to energy options: case study of KARTAMANTUL region, Yogyakarta. Renew Energy 41:277–284

    Article  CAS  Google Scholar 

  • Hauschild M, Wenzel H (1999) Environmental assessment of products. Int J Life Cycle Assess 1:7–15

    Google Scholar 

  • Hong JL, Li XZ, Cui ZJ (2010) Life cycle assessment of four municipal solid waste management scenarios in China. Waste Manag 30:2362–2369

    Article  CAS  Google Scholar 

  • Hu Q, Huang GH, Cai YP, Sun W (2014) Planning of electric power generation systems under multiple uncertainties and constraint-violation levels. J Environ Inform 23(1):55–64

    Article  Google Scholar 

  • Huang GH, Brian WB, Gilles GP (1992) A grey linear programming approach for municipal solid waste management planning under uncertainty. Civ Eng Syst 9:319–335

    Article  CAS  Google Scholar 

  • Huang W, Dai LM, Baetz BW, Cao MF, Razavi S (2013) Interval binary programming for noise control within an urban environment. J Environ Inform 21(2):93–101

    Google Scholar 

  • ISO 14044 (2006) Environmental management - life cycle assessment - requirements and guidelines. International Organization for Standardization

  • Jiao AY, Li ZS, Wang L, Xia MJ (2013) Optimization for municipal solid waste treatment based on energy consumption and contaminant emission. Environ Sci Pollut Res 20:6232–6241

    Article  CAS  Google Scholar 

  • Khoo HH (2009) Life cycle impact assessment of various waste conversion technologies. Waste Manag 29:1892–1900

    Article  CAS  Google Scholar 

  • Li YP, Huang GH (2010) An interval-based possibilistic programming method for waste management with cost minimization and environmental-impact abatement under uncertainty. Sci Total Environ 408:4296–4308

    Article  CAS  Google Scholar 

  • Li YP, Huang GH, Yang ZF, Nie SL (2008) An integrated two-stage optimization approach for the development of long-term waste management strategies. Sci Total Environ 392:175–186

    Article  CAS  Google Scholar 

  • Li YP, Huang GH, Yang ZF, Chen X (2009) Inexact fuzzy-stochastic constraint-softened programming—a case study for waste management. Waste Manag 29:2165–2177

    Article  CAS  Google Scholar 

  • Miao DY, Huang WW, Li YP, Yang ZF (2014) Planning water resources systems under uncertainty using an interval-fuzzy de novo programming method. J Environ Inform 24(1):11–23

    Google Scholar 

  • Ministry of Housing and Urban - rural development (2010) China urban construction statistics yearbook. China planning press, Beijing, pp 582–588 (In Chinese)

    Google Scholar 

  • Morselli L, Bartoli M, Bertaccchini M, Brighetti A, Luzi J, Passarini F, Masoni P (2004) Tools for evaluation of impact associated with MSW incineration: LCA and integrated environmental monitoring system. Waste Manag 25:191–196

    Article  Google Scholar 

  • National Bureau of Statistics of China (2010) China statistical yearbook. China statistical press, Beijing (In Chinese)

    Google Scholar 

  • National Development and Reform Commission of China (2012) Available at http://www.sdpc.gov.cn/zcfb/zcfbtz/2012tz/t20120410_472395.htm (In Chinese).

  • Ning SG, Chang NB, Hung MC (2013) Comparative streamlined life cycle assessment for two types of municipal solid waste incinerator. J Clean Prod 53:56–66

    Article  CAS  Google Scholar 

  • Özeler D, Yetis U, Demirer GN (2006) Life cycle assessment of municipal solid waste management methods: Ankara case study. Environ Int 32:405–411

    Article  Google Scholar 

  • Suo MQ, Li YP, Huang GH, Deng DL, Li YF (2013) Electric power system planning under uncertainty using inexact inventory nonlinear programming method. J Environ Inform 22(1):49–67

    Article  Google Scholar 

  • Tabata T, Hishinuma T, Ihara T, Genchi Y (2010) Life cycle assessment of integrated municipal solid waste management systems, taking account of climate change and landfill shortage trade-off problems. Waste Manag Res 29:423–432

    Article  Google Scholar 

  • Takeda N, Takaoka M (2013) An assessment of dioxin contamination from the intermittent operation of a municipal waste incinerator in Japan and associated remediation. Environ Sci Pollut Res 20:2070–2080

    Article  CAS  Google Scholar 

  • TSNPC (2010) Available at http://www.bjstats.gov.cn/tjnj/rkpc-2010/indexch.htm (In Chinese)

  • Xi BD, Su J, Huang GH, Qin XS, Jiang YH (2010) An integrated optimization approach and multi-criteria decision analysis for supporting the waste-management system of the City of Beijing, China. Eng Appl Artif Intel 23:620–631

    Article  Google Scholar 

  • Zhao Y, Christensen TH, Lu WJ, Wu HY, Wang HT (2011) Environmental impact assessment of solid waste management in Beijing City, China. Waste Manag 31:793–799

    Article  Google Scholar 

Download references

Acknowledgments

This research was supported by the Natural Sciences Foundation of Beijing (8122038), the National Natural Science Foundation (51225904), the 111 Project (B14008), and the Program for Innovative Research Team in University (IRT1127). The authors are grateful to the editors and the anonymous reviewers for their insightful comments and suggestions.

Author information

Authors and Affiliations

Authors

Corresponding author

Correspondence to Y. P. Li.

Additional information

Responsible editor: Philippe Garrigues

Rights and permissions

Reprints and permissions

About this article

Check for updates. Verify currency and authenticity via CrossMark

Cite this article

Li, P., Li, Y.P., Huang, G.H. et al. Modeling for waste management associated with environmental-impact abatement under uncertainty. Environ Sci Pollut Res 22, 5003–5019 (2015). https://doi.org/10.1007/s11356-014-3962-9

Download citation

  • Received:

  • Accepted:

  • Published:

  • Issue Date:

  • DOI: https://doi.org/10.1007/s11356-014-3962-9

Keywords

Navigation