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Magdalena

Rybaczewska-Błażejowa

Economic, Environmental and Social

Aspects of Waste Management – the

LCA Analysis

Prace Naukowe Akademii im. Jana Długosza w Częstochowie. Pragmata tes Oikonomias 7, 239-250

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PRACE NAUKOWE Akademii im. Jana Długosza w Częstochowie

Pragmata tes Oikonomias 2013, z. VII

Magdalena RYBACZEWSKA-BŁAŻEJOWSKA

Politechnika Świętokrzyska

Economic, Environmental and Social Aspects

of Waste Management – the LCA Analysis

Summary: The intention of this article is to discuss the theoretical and practical aspects of the life

cycle assessment (LCA) and its application in the modelling of waste management. The research was conducted with the use of the LCA-IWM software for the Ciechanowski Region of Municipal Waste Management, Mazovia Voivodeship. Three scenarios of municipal waste management have been analysed during the research – the municipal waste management system being currently in force (after 1st July 2013) and two fulfilling the Waste Management Plan for Mazovia 2012–2023.

Following the concept of sustainability, the scenarios were compared in terms of environmental, economic and social aspects. The research proved that both proposed scenarios have considerable lower environmental impacts than the one being currently in force in the city of Ciechanow. Si-multaneously, however, these scenarios generate higher costs per household and per 1 Mg of proc-essed waste. In terms of the social indicators, the three scenarios are comparable. In conclusion, taking into account all indicators of sustainability, two proposed scenarios (scenario 2 and scenario 3) enable to satisfy the objectives of waste management law at commensurate costs and social ac-ceptability.

Keywords: Sustainability, life cycle assessment (LCA), waste management, Poland.

Introduction

Life cycle assessment (LCA) is one of the methods of life cycle sustainabil-ity analysis (LCSA) that allows the evaluation of integrated waste management strategies from the point of waste generation and collection up to the final recov-ery and disposal. The application of LCA to the analysis of waste processes is still, however, very limited due to numerous barriers including data source and intensity, costs, poor information transfer, and finally time and expertise re-quired to run the LCA procedures. Considering the above, some support for practitioners might bring the research described in the article. The aim of the re-search was to critically compare the three possible scenarios for waste manage-ment for the city of Ciechanow with the use of LCA technique. Consequently,

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240 Magdalena RYBACZEWSKA-BŁAŻEJOWSKA

the article discusses the assessment criteria to measure environmental, economic and social sustainability in the specific case study.

1. The idea of sustainability in waste management

Sustainable development can be perceived as such socio-economic devel-opment, in which there is a process of integrating political, economic and social aspects with maintaining environmental balance and the sustainability of natural processes, in order to meet the needs of current and future generations (cf. [1]). Consequently, the pillars of sustainable development are economic prosperity, environmental protection and social equity (see figure 1).

Environmental sustainability in municipal waste management can be defined through two major objectives, which are conservation of resources and reduction of environmental pollution (cf. [3]). Sample indicators for the environmental sustainability in waste management are the conservation of resources through the collection of secondary raw materials, air emissions, fuel and electricity con-sumption, noise (cf. [9]).

Economic sustainability in municipal waste management can be defined as such integration of waste management options as to operate them at the lowest possible cost – acceptable to the community, local government and a municipal waste treatment facility itself. Sample indicators for the economic sustainability in waste management are the investment costs, the annual maintenance costs, personnel employment costs and finally revenues from recovered materials and energy.

Social sustainability in municipal waste management can be defined as pro-vision of appropriate level of waste services to meet health and comfort re-quirements of participants. Sample indicators for the social sustainability in waste management are the convenience of use, visual impact, odour, noise, and traffic nuisance (cf. [3]).

Following the Directive 2008/98/EC, all EU Member States “shall take into account the general environmental protection principles of precaution and sus-tainability, technical feasibility and economic viability protection of resources as well as the overall environmental, human health, economic and social impacts” while managing their waste (cf. [4]). Thus, only communes that fulfill the foun-dations of environmental, economic and social sustainability can claim that offer the integrated waste management services. To achieve the trade-off between the above is, however, a very challenging task.

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242 Fig. 2. Mod Source: Arn Goal (LCA). It are determ its functio the study applicatio energy co system bo a product Life c (LCA). It a given pr signed to draw up a lected fro emissions estimated Life c sessment Ma

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the third pha between the KA life cycle a ns; the most f a product s he system. T way as to th s a set of ma defined func t processes a life cycle a nputs and o uts and outp s carried out als and chem hat leave the measured, cal ase of the life e environmen assessment important system and The goal of he intended aterial and ctions. The are part of assessment outputs for

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inven-Economic, Environmental and Social Aspects… 243 tory and defined impact categories, and category indicators. Consequently, the

mandatory elements of that stage are as follows:

— selection of impact categories, category indicators and characterisation models, — assignment of LCI results to the impact categories (classification),

— calculation of category indicator results (characterisation).

In practice, due to the fact that the LCIA phase is very complicated, there are adequate computer programs, ad exemplum simapro, umberto, LCA-IWM to support the analysis.

Life cycle interpretation is the last phase of the life cycle assessment

(LCA). It is a procedure for the identification, qualification, verification and evaluation of the information obtained in the previous two phases (LCI and LCIA). Therefore, this phase ought to explain the limitations of the analysis as well as to enable the formulation of conclusions and recommendations regarding the reduction of environmental impacts.

To confront the environmental performance with economic and technical as-pects, the technique of LCA can be supported by the procedure of multi-criteria decision analysis (MCDA). This is a formalised and structured process for se-lecting between alternatives, basing the decision on several criteria. In the case of integrated waste management systems, the criteria encompass environmental, economic and social sustainability.

To make the LCA analysis of waste management for the city of Ciechanow, the LCA-IWM programme will be applied. The LCA-IWM programme was de-veloped within the European Programme entitled “The use of life cycle assess-ment tool for the developassess-ment of integrated waste manageassess-ment strategies for cit-ies and regions with rapid growing economcit-ies (LCA-IWM). It enables to enter the current environmental (ex. waste quantity and quality), economic and social indicators (ex. population age, average household size, gross domestic product per capita) into the programme. According to the authors from European univer-sities, ad exemplum Technical University Darmstadt (TUD), the LCA-IWM programme was tested in 55 European cities and this makes it credible (cf. [2]).

3. Case study – a description of waste management scenarios

The city of Ciechanow is a medium size city, located in the central part of Po-land in the Mazovia voivodeship. The city has around 45 000 inhabitants; 52% of the population are women. There are approximately 21000 Mg of municipal waste generated in Ciechanow yearly that gives 469 kg per person (Municipal Waste Treatment Facility in Ciechanow) (see table 1). The whole population of the city is covered by the municipal waste collection with some sort of separate waste collec-tion that is at the level below 10%. Disposal at the landfill site remains the predomi-nant form of municipal waste management. The city of Ciechanow is a member of the Association of Communes from the Ciechanow Region.

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244 Table 1. Ge Paper and c Glass Metals Plastics Organic wa Hazardous WEEE Bulky wast Other Municipal s Source: own Three elled for t Scenario This i before an ment facil lectively a metals, an landfilling is sorting garden wa Fig. 3. Scen Source: own Ma eneration of mu Waste fraction cardboard aste waste te

solid waste (in n research upon e following s the city of Ci 1 is the munic nd after 1st Ju

lity from Cie at source wit nd the remai g at the sanit of dry recy aste) (see fig

nario 1 – the cur n research. agdalena RYBA unicipal waste in n total) n the data of Mu scenarios of iechanow. cipal waste m uly 2013. Th echanow (PU th the divisio ining. Regard tary landfill s clables and gure 3). rrent municipal ACZEWSKA-B n Ciechanow in Mass [tons 4300 2000 600 2300 6900 100 400 100 4400 21100 unicipal Waste municipal w management he system is UK Sp z o.o. on for paper ding the mun site in Wola composting l waste managem BŁAŻEJOWSK n 2011 s/year] 0 0 0 0 0 0 Treatment Faci waste manage system bein run by the .). Municipal r and cardboa nicipal waste Pawlowska of biodegrad ment system in KA Mass [kg/ca 95 44 13 52 155 2 9 1 98 469 ility in Ciechan ement have b ng currently municipal w l waste is co ard, glass, pl e processing (PUK Sp z o dable waste

n the city of Cie

ap/year] now. been mod-in place – waste treat-ollected se-lastics and g – besides o.o.), there (primarily echanow

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Economic, Environmental and Social Aspects… 245

Scenario 2

It was assumed that the municipal waste management system would be such organised as to fulfil the foundations of the Waste Management Plan for Ma-zovia 2012–2023. To meet its objectives, municipal waste will be still collected selectively at source and subsequently processed in the regional facility in Wola Pawlowska. In three years time at the latest, the facility ought to offer:

— the semi-automatic sorting processes together with the production of refused derived fuel, having the capacity of 65 thousand tonnes of municipal waste annually,

— aerobic processing of 30 thousand tonnes of the organic fraction of munici-pal waste yearly in the BIODEGMA in-vessel system to produce compost, — deposition of municipal solid waste residues at the sanitary landfill site

equipped with a leachate collection system and a landfill gas control system converting landfill gas into energy.

Scenario 3

The municipal waste management system in the third scenario is another op-tion for fulfilling the objectives of the Waste Management Plan for Mazovia 2012–2023. To meet its objectives, municipal waste will be still collected selec-tively at source but will be processed in the regional facility in Kosiny Barto-sowe and Uniszki-Cegielnia (USKOM Sp z o.o.). The facility offers:

— the semi-automatic sorting processes having the capacity of 250 thousand tonnes of municipal waste annually,

— an installation for bio-stabilisation of municipal waste having the capacity of 100 thousand tonnes of municipal waste annually,

— deposition of municipal solid waste residues at the sanitary landfill site equipped with a leachate collection system and a landfill gas control system converting landfill gas into energy.

4. Results – the life cycle impact assessment (LCIA)

The life cycle assessment (LCIA) provides the comparison of the scenarios in terms of their environmental, economic and social impacts. Due to lack of the necessary information on the planned re-construction of the municipal waste treatment facility in Wola Pawłowska, this stage has been excluded from the analysis. Chosen results of the research are presented below.

The environmental impacts of the scenarios were presented with the use of the following impact categories recommended by CML 2001 method:

— depletion of abiotic resources, — global warming

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246 — photo — acidif — eutrop Enviro residents t tion are th for a perio crease in burden (se Fig. 4. Envi Source: own Consi siderably of global tion of th biological able to fu degradabl Ma -oxidant form fication, phication. onmental im that are spec he equivalent od of one ye environmen ee figure 4). ironmental imp n research. idering the e lower impac warming, ac he waste ma l processing. ulfil the legal le waste bein

agdalena RYBA

mation, mpacts are pre

cific to each t emissions r ear and a citi ntal impacts,

acts of the anal

environmenta cts than the s cidification a anagement t . Furthermor l requiremen ng landfilled ACZEWSKA-B esented in th category of i representativ izen of Euro whereas po lysed scenarios al aspects, b scenario 1. Th and eutrophic technology f re, only the

ts, for instan (see figure 5

BŁAŻEJOWSK

he form of an impact. The ve for the giv ope. Negative

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both propose he greatest d cation. The r from landfil second and t nce, in reduc 5). KA n equivalent basis for the ven category e values indi s reveal envi Ciechanow ed scenarios differences ar reason is the lling into m the third sce ing the amou

number of eir calcula-calculated icate a de-ironmental have con-re in terms modifica- mechanical-enarios en-unt of

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bio-Fig. 5. Amo versus the a Source: own The e lysed with narios gen the one th most sign managem from reco Table 2. Com A per 1 Mg o per househo per person Revenue fr als and ener The differe and expend waste mana Source: own E ount of biodegr analysed scenari n research. conomic issu hin the resea nerate higher hat is current nificant seem ment. Simulta overed materi mparison of the Annual cost f waste (€/Mg) old (€/capita) (€/person) om recovered m rgy (€) nce between re ditures of munic agement (%) n research. Economic, Envir adable waste la ios for the city

ues related to arch (see tabl

r costs per ho ly operating. ms to be aga aneously, how

ials and ener

economic effici Sc materi-evenues cipal ronmental and S andfilled (as % of Ciechanow o municipal le 2). The stu ousehold and . Although, t ain the altera wever, these rgy.

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cenario 1 28 38 14 14 161 183 Social Aspects… of biodegradab waste mana udy proved th d per 1 Mg o there are plen ation of the two scenario lysed scenarios f Scenario 2 45 62 22,4 110 354 111

ble waste produ

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2 Sce 2 10 247 uced in 1995) e also ana-posed sce-waste than for that the for waste er revenue iechanow nario 3 47 64 23,7 00 115 107

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248 Fig. 6. Soci Source: own The s each scen siderable From the the value ployment such soci space con the munic visual imp the one w is respons

Conclus

The c On the on of life cy optimising Although cision pro Ma al indicators of n research. social indica nario and pha differences social point 1 the worst s rate or nois al indicators nsumption. T cipal waste tr pact and the with MBP ins sible for the u

sions

ompletion o ne hand, the cle assessme g of waste m LCA metho ocess and ena

agdalena RYBA f the analysed sc ators of mun ase individua in most soc t of view the situation. Co e are compa s as the visu The second sc reatment fac space consu tallation loca utmost traffi f described r study prove ent (LCA) c management od is not free ables to redu ACZEWSKA-B

cenarios for the

nicipal waste ally. The rese cial factors e value 0 rep onsequently, arable for eac

ual impact, t cenario – the ility in Wola umption. On t ated approx. c difficulties research brou ed that the en ould be app t systems fr e of shortcom uce the risks

BŁAŻEJOWSK e city of Ciecha e manageme earch proved between sce presents the the social in ch scenario. the traffic nu one that em a Pawlowska the other han

30 km from s.

ught multidim nvironmenta

lied for both rom the sust mings, it defi of mismana KA anow ent were an d that there a enarios (see best situatio ndicators of o The differen uisance and mploys the exp

a generates th nd, the third m the city of C mensional ad al manageme h the plannin tainability pe initely suppo agement of w nalysed for are no con-figure 6). on whereas odour, em-nces are in the urban pansion of he greatest scenario – Ciechanow dvantages. ent method ng and the erspective. orts the de-waste

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man-Economic, Environmental and Social Aspects… 249 agement systems and related to it serious environmental, financial and social

consequences (cf. [9]). Furthermore, the applied programmes for conducting the life cycle impact assessment (LCIA) give the opportunity to review the analysed systems in meeting the stringent requirements of the waste law. On the other hand, the research examined the specific case study of the waste management system for the city of Ciechanow. Taking into account all indicators of sustain-ability – environmental, economic and social, only the scenario 2 and 3 are able to satisfy the objectives of waste management law at commensurate costs and social acceptability. The reason is that only these two scenarios offer the ade-quate waste processing in the form of mechanical-biological treatment.

Literature

[1] Act of 27 April 2001 Environmental Protection Law.

[2] Den Boer (Szpadt) E., Den Boer J., Jager J., The use of life cycle assessment tool for the development of integrated waste management strategies for

cit-ies and regions with rapid growing economcit-ies LCA-IWM, Technische

Universität Darmstadt, Darmstadt 2005.

[3] Den Boer J., Sustainability Assessment for Waste Management Planning – Development and Alternative Use of the LCA-IWM Waste Management Sys-tem Assessment Tool – PhD Dissertation, Technische Universität Darm-stadt, Darmstadt 2007, p. 17–88.

[4] Directive 2008/98/EC of the European Parliament and of the Council of 19 November 2008 on waste and repealing certain Directives.

[5] ISO 14040:2006 Environmental management – Life cycle assessment – Principles and framework.

[6] ISO 14044:2006 Environmental management – Life cycle assessment – Re-quirements and guidelines.

[7] Morrissey A.J., Browne J., Waste management models and their application to sustainable waste management, “Waste Management” 24 (2004), El-sevier 2004, p. 297–308.

[8] Tukker A., Handbook on Life Cycle Assessment, Kluwer Academic Publish-ers, New York – Boston – Dordrecht – London – Moscow 2002, p. 19. [9] Schluchter W., Rybaczewska-Błażejowska M., Life cycle sustainability

as-sessment of municipal waste management systems, “Management”, Univer-sity of Zielona Góra, Zielona Góra 2012, p. 311–322.

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250 Magdalena RYBACZEWSKA-BŁAŻEJOWSKA

Ekonomiczne, środowiskowe i społeczne aspekty zarządzania

gospodarką odpadami – analiza techniką LCA

Synopsis: Celem niniejszego artykułu jest przedstawienie podstaw teoretycznych oraz praktyczna

aplikacja narzędzia zarządzania środowiskowego, jakim jest ocena cyklu życia (LCA), w modelo-waniu gospodarki odpadami. Badanie wykonano z wykorzystaniem oprogramowania LCA-IWM dla ciechanowskiego regionu gospodarki odpadami, gmina Ciechanów, woj. mazowieckie. Anali-zie poddano trzy możliwe scenariusze gospodarki odpadami – aktualnie obowiązujący (po 1 lipca 2013 r.) oraz dwa zgodne z Wojewódzkim Planem Gospodarki Odpadami dla Mazowsza na lata 2012–2017 z uwzględnieniem lat 2018–2023. Zgodnie z założeniami koncepcji zrównoważonego rozwoju, scenariusze porównano pod kątem aspektów środowiskowych, ekonomicznych i spo-łecznych. Badania pokazały, iż oba proponowane scenariusze (scenariusz 2 i scenariusz 3) mają znacznie niższe oddziaływania środowiskowe niż aktualnie realizowany system gospodarki odpa-dami w mieście Ciechanów. Równocześnie jednak oba powyższe scenariusze generują znacznie wyższe koszty w przeliczeniu na gospodarstwo domowe i Mg odpady. Ze społecznego punktu wi-dzenia scenariusze nie wykazują istotnych różnic. Reasumując, mając na uwadze wszystkie anali-zowane wskaźniki zrównoważonego rozwoju, należy stwierdzić, iż tylko scenariusz 2 i scenariusz 3 zapewnia realizację celów prawa gospodarki odpadami przy stosunkowo umiarkowanych kosz-tach i akceptowalności społecznej.

Słowa kluczowe: Zrównoważony rozwój, ocena cyklu życia (LCA), zarządzanie gospodarką

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