Alexander Ișcenco
Supervised by Iben Nathan
Funded by
the Explorers Club Exploration Fund
Non-state Cooperation in Environment Protection Area: A Solution for Waste Management in the
Republic of Moldova
Copenhagen 2012
University of Copenhagen
Non-state Cooperation in Environment Protection Area: A Solution for Waste Management in the Republic of Moldova
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Chapter I
Why is waste an important issue to be addressed?
The chapter includes:
1.1 Brief description of
waste types;
1.2 Their impact on the
environment, economy
and human health.
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Chapter II
How can waste be managed efficiently?
The chapter includes:
2.1 Explanation of the waste
hierarchy;
2.2 Present relevant waste
management policy
instruments;
2.3 Reveal some specifics of
the waste management
market.
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Chapter III
Why is waste management and governance a problem in Moldova?
The chapter includes:
3.1 Brief description of the
Republic of Moldova;
3.2 Waste generation and
accumulation there;
3.3 State of the waste
management market;
3.4 Reasons of inefficiency
in waste management;
3.5 Negative consequences
of it for Moldova.
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Chapter IV
Why should private companies and NGOs be involved in waste management?
The chapter includes:
4.1 Characteristics and
reasons of involvement
of private companies;
4.2 Main strong points and
contribution of
environmental and
other NGOs.
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Chapter V
How can non-state actors work together to address the waste issue?
The chapter includes:
5.1 Definition and motives
for non-state
cooperation;
5.2 Comparison of its
advantages and
disadvantages;
5.3 Process of cooperation
development;
5.4 Good case practices.
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Chapter VI
How can the waste issue in Moldova be solved through non-state cooperation?
The chapter includes:
6.1 Data collected and used
for modelling non-state
cooperation in Moldova;
6.2 Theories and methods
applied in the model;
6.3 The model framework
of non-state cooperation
development;
6.4 Practical implications of
the model in Moldova;
6.5 Application of the model
to the example of “Hai,
Moldova!”
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Chapter VII
Chapter VII
What are the applications and limitations of the present work?
The chapter includes:
7.1 Potential of applying the
model and the whole
research to other
similar countries;
7.2 Limitations of the model
and the work that
require further
research.
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ANNEX
Tables.
Table A1 – Main Types of Waste Based on Their Source and Composition.
# Type Major Sources Composition Share in Total Quantity
1. Municipal Solid and Biodegradable Waste (MSW and MBW)
Households, tourism, commercial enterprises, NGOs, state authorities, etc.
Paper and cardboard, organic material (food and garden waste), glass, plastics, textiles, wastewater.
Approximately 14% of all waste generated.
2. Packaging Waste Households, industry, tourism, commercial enterprises, NGOs, state authorities, etc.
Glass bottles, plastic containers, aluminium cans, food wrappers.
In the range of 17 – 20%.
3. Industrial Waste Manufacturing companies and state-owned enterprises.
Metals, plastic, various gaseous and liquid chemicals, waste from energy production.
Ranges from 30% to 60%.
4. Construction and Demolition Waste
Construction, demolition, and infrastructure maintenance enterprises.
Concrete, bricks, wood, glass, metals, plastic, solvents, asbestos, asphalt, excavated soil.
About 25 – 30%.
5. Mining Waste Mining sites, quarries, and minerals treatment and storage facilities.
Topsoil, overburden, waste rock, sulfur, waste from processing of the ore body (tailings).
Around 29%.
6. Agricultural Waste Farmlands, agricultural enterprises.
Organic waste (slurry, manure), pesticides, plastic, veterinary medicines, waste water.
Up to 60 – 80%.
7. Waste from Electrical and Electronic Equipment (WEEE, or e-waste)
Households, industry, commercial enterprises.
Televisions, cell phones, computers, refrigerators and other equipment.
Approximately 4%.
8. End-of-Life Vehicles (ELV) and Tyres
Households, industry, commercial enterprises.
Used cars, trucks, lorries, and their components.
Nearly 3 – 5%.
9. Hazardous Waste Households, industry, commercial enterprises, military facilities.
Dangerous chemicals, batteries, medical waste, military waste, radioactive substances.
About 1 – 3%.
10. Space Waste Space industry, space research institutions, military facilities.
Operational and non-operational spacecraft, rocket bodies, and their fragments, space equipment items.
Unknown.
Source: elaborated by the author, based on Eionet (2009) and Letcher et al. (2011)
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Table A2 – Brief Country Profile of the Republic of Moldova, 2011 – 2012.
# Parameters Description
Geography 1. Area 33,843.5 km2, where 11% is covered by forests and 1.4% - by water 2. Highest point Bălănești Hill (429.5 m) 3. Main soil types Black soil / chernozem (75%); alluvial meadow soils (12%); brown
and gray forest soils (11%) 4. Main water resources Rivers Dniester, Prut, and Răut 5. Natural resources Arable land, gypsum, lignite, limestone, phosphorites 6. Climate Temperate continental with average temperature range from +20oC to -
4oC and precipitation of 600 mm 7. Biodiversity 5,500 species of plants and 15,500 species of animals
Administration 8. Capital Chișinău (789,500 residents) 9. Other large cities Tiraspol (148,900 residents); Bălți (144,300); Cahul (39,700) 10. Government Parliamentary republic 11. Independent since 27th of August, 1991
Society 12. Population 3,560,430 inhabitants with the density of 117 people per km2 13. HDI 0.649 (medium Human Development Index) 14. Poverty rate 29% of all population 15. Median age 35.4 years (men – 33.5 years, women – 37.4 years) 16. Life expectancy 69.3 years (men – 65.3 years, women – 73.5 years) 17. Ethnic groups Moldovans – 76%; Ukrainians – 8%; Russians – 6%; Gagauzes – 4%;
Romanians – 2%; Bulgarians – 2%; Others – 2% 18. Official language Romanian 19. Major religion Christianity
Economy 20. GDP 12.04 bln USD (PPP); 7.2 bln USD (nominal) 21. GDP per capita 3,383 USD (PPP); 2,022 USD (nominal) 22. GDP growth 6% 23. Public debt 19.3% of GDP 24. Inflation 8.1% 25. Unemployment 7.4% 26. Currency Moldovan Leu (MDL): 1 MDL ~ 0.08 USD ~ 0.06 EUR ~ 0.48 DKK 27. Gini coefficient 37.1 (very high inequality of family income) 28. Main economic
activity Agriculture and food processing (40% of GDP; 60% of land)
29. Main exports Foodstuff, animal and vegetable products, textiles 30. Main imports Mineral products, base metals, machinery and electrical equipment
Business 31. Ease of Doing
Business Index 81 (starting a business rank – 88, closing business / resolving insolvency – 91)
Source: elaborated by the author, based on
BBC (2012); CIA (2012); Iscenco (2011c); National Bureau of Statistics (2011);
Republic of Moldova – Official Website (2011); The World Bank (2012a)
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Table A3 – Notations for the Model of Non-state Cooperation in Waste Management. # Symbol Definition Explanation
1. A Adoption costs Costs associated with time requirements to obtain, adapt and implement the inputs from cooperation.
2. B Benefits Total direct benefits an economic agent gains from joining the alliance.
3. b Cost reduction Percentage reduction in cost per unit of effort and/or output. 4. C Total costs Total costs of an economic agent. 5. c Costs per unit Costs per unit of output produced by an economic agent. 6. d Disposable waste Waste that is going to be disposed to a landfill or
incinerated. 7. E Efficiency gain Internal efficiency gain to an economic agent. 8. h Waste management
costs Costs of collecting, sorting, storing, and treating waste streams.
9. j Non-state actor An economic entity represented by company or NGO. 10. k Opponent An economic entity opposing the decisions and efforts of j. 11. M Monitoring costs Costs necessary to encourage members do their part and
prevent or punish free-riders within the alliance. 12. N Benefits of
monitoring Avoidance of lost benefits and additional costs, because other alliance members do not practice shirking.
13. n Number of participants
Total number of non-state actors participating in a cooperation framework.
14. P Penalty costs Punishment incurred by an alliance member when it is caught shirking.
15. Q Output Total output of a company / NGO. 16. r Reusable /
recyclable waste Waste that will be either reused one or more times or recycled into resources for production.
17. S Benefits from shirking
Total benefits gained by an economic agent from shirking / free-riding on other alliance members’ contributions.
18. T Contribution costs Costs related to continuous participation in the alliance. 19. t Time Any given point in time. 20. u Waste reuse rate Average number of times waste from a unit of good
has been reused as inputs for producing another unit. 21. V Valuation of a
favourable outcome Economic agent’s valuation of a favourable outcome as a result of its efforts.
22. x Sensitivity of outcome
Means by which efforts and pressures from different sides are converted into a certain political, legislative, economic, social, or environmental outcome.
23. α Coefficient of shirking
Proportionate reduction in contributions made by an economic agent to the cooperative activities (here 0 means no shirking, 1 – complete shirking).
24. γ Adoptable productivity improvements
Fraction of partners’ productivity improvements that can be successfully incorporated by other adopters.
25. π Profit / net gains Expected value of net gains to an economic agent. Source: elaborated by the author, based on
Coskeran et al. (2006) and Grimes-Casey et al. (2006)
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Figures.
Figure A1 – Waste Generation and Composition in Selected Countries, mln metric t.
Source: Letcher et al. (2011)
Figure A2 – Period of Decay for Some of the Waste Products, years.
1
5
5
40
50
50
80
400
800
1000
1000
4000
0 200 400 600 800 1000 1200
Paper
Cigarette filter
Leather
Boot sole
Monofilament fishing line
Plastic card
Source: elaborated by the author, based on Green Living (2009);
Green Living Tips (2010); Hotărîre Nr. 35 din 01.06.2010; Iscenco, A. (2011b)
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Figure A3 – Ecological Footprint and Available Biocapacity per Capita in Europe.
Source: EEA (2010)
Figure A4 – EU-27 GHG Emissions by Sector in 1990 and 2009.
Source: UNFCCC (2010)
Figure A5 – Generation of the Two Most Impactful GHG in Landfilled Waste.
Source: Letcher et al. (2011)
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Figure A6 – Comparison of Waste Generation and Recycling among the Regions.
Source: elaborated by the author, based on
IPCC (2011); Iscenco (2011d); Letcher et al. (2011); Worldmapper (2011)
Figure A7 – Location, Map and Flag of the Republic of Moldova.
Source: elaborated by the author, based on Republic of Moldova – Official Website (2011)
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Figure A8 – Main Soil Types of the Republic of Moldova.
Source: UNEP/GRID-Arendal (2005)
Figure A9 – Ecological Footprint versus Global Available Biocapacity per Person, 2003.
Source: EEA (2007)
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Figure A10 – Management of Hazardous Waste in Selected Countries, 1995 – 2004.
Note: The category “Other” covers different kinds of disposal activities, i.e. not recovery
treatment. Release into water bodies and permanent storage are included here.
Source: EEA (2007)
Figure A11 – Growth of the Landfill Area in Moldova and Waste Disposed There.
1103 1232 1304 1355 1306 1300 1350 1402 1415
6062
14190
19210
28952 29500 30000 3150033630
45727
0
5000
10000
15000
20000
25000
30000
35000
40000
45000
50000
2001 2002 2003 2004 2005 2006 2007 2008 2009
Landfill Area, ha Volume of Waste, thousand m3
Source: Iscenco (2011c); Hotărîre Nr. 35 din 01.06.2010
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Figure A12 – Problem Tree for Waste Management in Moldova.
Source: elaborated by the author, based on Particip.gov.md (2012)
Lack of waste management
companies in the majority of locations
Inefficient Waste Management
Inadequate infrastructure for quantifying and eliminating
waste
Insufficient monitoring and
control over waste
management practices
Residents are not informed
about the issue and waste
management practices
Low investments in developing waste
management
Local instruments for financing waste
management are not used
Inefficient public awareness raising and
informative programmes
Small size of waste management market, thus
it is not so attractive
Low administrative capacity to handle the
waste issue
Incomplete and inefficient legislative basis for waste
management
Reduced access to waste management services for
population
Creation of unauthorized waste dumps
Low economic value of waste and thus reduced
recycling rate
Waste of financial and
other resources for “liquidating”
illegal dumps
Increasing amounts of
waste disposed to landfill sites
Reduced recovery of
valuable resources and
energy
Pollution of the environment, including soil, water, and air
Overloading and reduced duration of exploitation of
landfill sites
Negative effects on human health and thus increased
morbidity rate
Negative effects on land and thus on agricultural and touristic activities
Necessity of financial and other resources for
constructing new landfills
Economic effects related to higher health costs, lower labour productivity, etc.
Reduction of the overall quality of life in the
country
P R O B L E M
R E A S O N S
C O N S E Q U E N C E S
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Figure A13 – Institutional System of Waste Management in Moldova.
Source: elaborated by the author, based on Hotărîre Nr. 35 din 01.06.2010
Figure A14 – Classification of Waste in Moldova Based on Its Toxicity, t, 2002 – 2003.
2215
695
940
5202
0 1000 2000 3000 4000 5000 6000
Class IV - Reduced Toxicity
Class III - ModerateToxicity
Class II - High Toxicity
Class I - Extremely Toxic*
Note: *Class I waste has been significantly reduced since 2003.
Source: elaborated by the author, based on
State of the Environment in the Republic of Moldova (2004)
Parliament
Government
Ministry of the Environment
Ministry of Construction and Regional Development
Ministry of Health
State Ecological Inspection
Sanitary and Epidemiologic Service
Public Administration Authorities
Physical and Juridical Persons
Waste
Delegation of tasks Collaboration Control over waste management Waste management process (generation, collection, transportation, disposal, incineration)
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Figure A15 – Stakeholders for Efficient and Sustainable Municipal Waste Management.
Source: elaborated by the author, based on Joseph (2006)
- Keep waste management as priority; - Provide infrastructural inputs and services; - Have a definite organizational setup with trained staff; - Implement legislation and punish violators; - Compliment public / private participation; - Involve the informal sector into participation; - Maintain an up-to-date database about waste management.
Municipalities - Keep waste management in mind while developing city plans; - Demarcate space for waste management facilities with ideal buffer zones.
City Planners - Lead the cleanup campaigns and work in unison towards the interest of a clean city; - Pressure the municipalities to make the waste management issue a priority; - Do not to turn the cleanup campaigns into a political issue.
Politicians
- Ensure that all employees understand the importance of the waste issue and not only take actions on the cleanliness front within the office/factory premises but also spread the message among their stakeholders; - Provide waste collection facilities outside office/company premises so that the passers-by do not throw waste on the street; - Support / sponsor cleanup campaigns.
Companies - Take lead in forming ward committees and ensuring community participation; - Network with other environmental organizations in the area and integrate their efforts; - Use existing contacts with the municipality and other influential bodies to ensure maximum support; - Involve unemployed youth in the area; - Organize / support cleanup campaigns.
NGOs
- Practice source reduction and source separation; - Cooperate with civic bodies in identification of sites for waste management facilities and their operation; - Pay for waste management services.
General Public - Influence minds on the culture of sustainable waste management; - Inculcate a strict discipline in the children’s mind with regard to waste; - Carry out relevant research and development.
Teachers / Academia - Take up various opportunities of part / full time employment that the NGOs and cleanup campaigns would open for them; - Separate waste; - Influence / keep check on parents / domestic servants.
Children / Youth
Municipal Waste Management
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Figure A16 – Advantages and Disadvantages of Non-State Cooperation in Waste Management and Governance.
Source: elaborated by the author, based on Heyes and Dijkstra (2001);
Johnson et al. (2012); Merchant (2011); O’Neill (2009)
ADVANTAGES:
1) The “first-mover advantage”: opportunity to create demand and be the first to obtain the segments and niches of a particular market, such as the buyers willing to pay a premium for goods produced in an environmentally friendly way (for instance, with biodegradable / recyclable packaging); 2) Gains from the diversity of horizontal and vertical linkages between a broad variety of economic agents (between corporations and international NGOs, their local branches and community groups, etc.); 3) Increase of the participants’ market power and resistance to threats; 4) Availability of significant lobbying and bargaining power of the strategic alliance; 5) Increase of resource use efficiency; 6) Faster and more effective exchange of the necessary information; 7) “Cross-pollination” of ideas and innovations among the partner organizations; 8) Making environmentally damaging practices more visible and the actors behind them more accountable to the society; 9) Engagement of broad public (through NGOs) in waste management and governance; 10) Creation of incentives for eco-friendly behaviour, but not necessarily with serious loss of profits; 11) Faster and more efficient use of market-based incentive mechanisms of waste management; 12) Possibility to close gaps between policy elaboration and its implementation in practice and thus enhance the activity of state actors; 13) Possible emergence of certification and labeling schemes (for instance, for goods made totally from reused / recycled materials); 14) State actors can avoid political and economic costs of regulation and control, especially in the areas where they represent a great challenge.
DISADVANTAGES:
1) Voluntary nature of participation – anyone can leave whenever he/she wants to or not participate at all (and the ones out of cooperation are usually organizations with the worst pollution record); 2) Weak mechanisms to ensure the external accountability of non-state actors, as well as lack of sufficient enforcement and control over their cooperation due to its voluntary nature; 3) Particularly demanding managerial processes within an alliance due to the lack of ownership and control by one side or another (especially in non-equity alliances); 4) Complicated and time-consuming negotiations process – “too much talking and not enough doing”; 5) Need for significant and increasing commitment of resources that could have been used in other possibly more productive activities, i.e. opportunity costs; 6) Problem of free-riding by certain members of an alliance; 7) Possibility of obtaining important information about partners and then using it to overthrow them from the market; 8) Uneven distribution of power and influence within an alliance – certain large corporations may well press on smaller and weaker partners to push forward their corporate interests; 9) Cooperation can become complex and conflictual – there is a risk that NGOs become co-opted in the corporate agenda they do not agree with; 10) Issue of inequity among the participants and even exclusion of small but high-value-adding ones if they do not accept the “rules of the strong”; 11) Non-state cooperation can serve as a way for state actors to avoid their responsibilities regarding waste management and governance.
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Figure A17 – Stages of the Non-state Cooperation Development.
Source: elaborated by the author, based on Johnson et al. (2012)
Figure A18 – Closed-loop system of the Kalundborg Symbiosis.
Source: VisitKalundborg.dk (2012)
Commitment of resources
Time
Courtship Negotiation Start-up
Addressing the demand
Maintenance Termination
Divorce / sale
Amicable separation
Extension
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Figure A19 – Countries Participating in “World Cleanup 2012” by “Let’s Do It!”.
Source: Let’s Do It! (2012)
Figure A20 – Activity Worksheet for the SWOT Analysis.
Source: elaborated by the author, based on Srivastava et al. (2004)
STRENGTHS:
- What are the advantages of cooperation? - What can the alliance do as well? - What are the factors supporting non-state cooperation in waste management?
WEAKNESSES:
- What could be improved? - What is not done properly? - What should be avoided? - What internal obstacles prevent progress? - Which elements need strengthening? - Are there any weak links in the cooperation system?
OPPORTUNITIES:
- Where are the good chances facing cooperation? - What are the interesting trends? - What benefits may occur? - What chances in waste management and governance may be possible? - What changes in socio-economic patterns, life-style, economic and environmental standards may occur?
THREATS:
- What external obstacles does the alliance face? - Are the required support and necessary facilities available? - Is the changing legislation, political situation or technology threatening the alliance? - Do the stakeholders show interest and willingness to engage in cooperative relations?
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Figure A21 – SWOT Analysis of Non-state Cooperation in Waste Management in the Republic of Moldova.
Source: elaborated by the author, based on interviews, survey and feedback
THREATS:
1) Not enough incentives to initiate cooperation; 2) Public demand insufficient to drive forward positive change in waste management; 3) Targeting and inclusion of inappropriate stakeholders in the future cooperation system; 4) Not agreeing on cooperation framework and thus no “sealing the deal”; 5) Shirking / free-riding and thus lack of trust among partners; 6) Cooperation can become complex and conflictual; 7) Exclusion of high-value-adding members; 8) Non-sustainability of cooperation system; 9) Shortness and non-achievements of cooperation; 10) Top-down style of governance and lack of certain legislation that make it challenging to cooperate in the area of waste management; 11) Little support and significant ignorance coming from other economic agents; 12) Small and highly monopolized market.
STRENGTHS:
1) The “first-mover advantage” - opportunity to create the demand and be the first to obtain a segment of the waste management market; 2) Increase of the participants’ market power; 3) Availability of significant lobbying and bargaining power of the strategic alliance; 4) Sharing of efforts and costs; 5) Increase of resource use efficiency; 6) More effective exchange of information; 7) “Cross-pollination” of ideas and innovations among the partner organizations; 8) Making environmentally damaging practices more visible and companies more accountable to society; 9) Creation of incentives for “eco-friendly” behavior; 10) Possibility to close gaps between policy elaboration and its implementation in practice and thus enhance the activity of state actors; 11) State actors can avoid political and economic costs of regulation and control.
WEAKNESSES:
1) Voluntary nature of participation; 2) Weak or no mechanisms to ensure the external accountability of non-state actors; 3) Particularly demanding managerial processes within an alliance; 4) Complicated and time-consuming negotiations process; 5) Need for significant and increasing commitment of resources; 6) Uneven distribution of power and influence within an alliance; 7) Participation of low-performing stakeholders in cooperation system; 8) Non-state cooperation can serve as a way for state actors to avoid their responsibilities regarding environmental management and governance; 9) Significant difficulty of establishing cooperation in rural areas.
OPPORTUNITIES:
1) Availability of environmental NGOs committed to improve waste management, large companies practicing CSR, and recyclers ready to accept waste; 2) Availability of reusable / recyclable waste, especially if source separation is established; 3) Possibilities of cooperation with state authorities; 4) Support from international organizations; 5) Engagement of broad public in waste management and cooperation activities; 6) Examples of successful non-state cooperation practices in waste management to capitalize on; 7) A large variety of opportunities to improve waste management services (such as waste monitoring, recycling, etc.) and benefit from it; 8) Possibility to avoid many state-related obstacles (such as corruption in state authorities); 9) Possibility to engage other economic agents through the evidence of waste pollution effects on the economy, environment and human health.
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Figure A22 – Recyclable Waste Generated in the Southern Development Region of Moldova in 2011, t.
Source: ADR Sud (2011)
Figure A23 – Selected Environmental Impacts in 2020 from the Use of Various MSW Management Practices in Chișinău, the Republic of Moldova.
Note: The values are related to the highest value within each impact category, i.e. if the
global warming impact of landfilling is equal to 100 % in 2020 then the value is only 30 %
for the two other scenarios.
Source: EEA (2007)
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Figure A24 – Graphical Version of the Model of Non-state Cooperation Development in Waste Management in Moldova.
Source: elaborated by the author
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Figure A25 – Guiding Version of the Model of Non-state Cooperation Development in Waste Management in Moldova.
Raising demand and creation of incentives
1) Is there any up-to-date information on generation and accumulation of waste and its effects on economy and human health available?
Establish waste monitoring and obtain relevant data
2) Are economic agents aware of the negative effects of waste pollution sufficiently enough to generate demand for better waste management?
Deliver messages through different channels
Courting potential partners
3) Is there any large economic agent with high stakes and power in waste management included as partners within the cooperation system?
Attract stakeholders with great interest and power
4) Is one or several participants of the cooperation system also a member within an international network of waste management companies/NGOs?
Establish or join an international network
Negotiation about cooperation system
5) Are there rules and procedures of negotiations understandable by all participants established before the actual negotiation process?
Set up clear negotiation rules and procedures
6) Is the positive value of the expected individual and common net gains from cooperation ensured and clearly visible to all negotiating parties?
Display positive net benefits of cooperation to all parties
- YES - NO - Key question - Key suggestion
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Source: elaborated by the author
Start-up of cooperation
7) Is there one or several large interested and powerful economic agents that agreed to cooperate and proceed with starting-up an alliance?
Involve additional large companies and NGOs
8) Is there an efficient system of monitoring the progress of cooperation and commitment of its members with high enough penalty costs in place?
Establish the monitoring and punishment systems
Maintenance of the alliance
9) Are there a number of heterogeneous alliance members sufficient enough to generate additional inflow of contributions and innovations?
Attract small- and medium-sized economic agents
10) Are contributions of all partners high enough to exceed the costs of their monitoring and thus maintain positive net benefits of the alliance?
Reduce number of partners or outsource monitoring
Termination of cooperation
11) Are there positive net benefits for all key players sufficient enough to keep them in the alliance until full realization of its purpose?
Reduce monitoring costs through external resources
12) Has the cooperation system achieved its purpose, vision, goals, etc. and delivered the intended improvements in waste management?
Maintain flow of benefits to keep the alliance
Start operating separately
Establish a new cooperation system
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Figure A26 – Quantity and Distribution of Participants of “Hai, Moldova!” in 2011.
Source: Hai, Moldova! (2011)
Number of participants, persons
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Figure A27 – Overview of Similarities and Differences in Waste Management in the EECCA and SEE Countries.
Source: EEA (2007)
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Interviews and Surveys.
Interview with Marc Zweig, Administrator at the Company AVE Ungheni SRL. 1
Details Interviewee Marc Zweig, administrator at AVE Ungheni SRL (www.ave.at) Interviewer(-s) Alexander Ișcenco, author of the research report;
Mihai Surdu, member of „Hai, Moldova!” (www.hai.md) Date 03.04.2012 Place Office of AVE Ungheni SRL
Națională 11, Ungheni, Republic of Moldova Summary
# Questions Key Notes from the Answers 1. Why did your
company come to the Moldovan market?
There is waste. There is no waste management system. Thus we came to offer our services of waste collection and treatment. Our first step was the city of Ungheni, as we had established the collaboration with the municipality here.
2. You have mentioned Ungheni as the first step. Do you intend to move forward to other cities?
Well, we are already present in other cities in Moldova. Chișinău, Durlești, Bubueci… You can se eon the map that we have spread to many cities and villages. (Mr Zweig shows the map of Moldova hanging on the wall with the AVE logo placed at the locations mentioned)
3. Do you experience any obstacles in operating and expanding in Moldova?
Umm… I don’t think this is the right place to talk about it…
4. AVE Ungheni has set up different containers for sorting waste. But how do you make people do the sorting?
Though education. We try to inform and educate people about waste management. We organize meetings with citizens, including the retired ones and children.
5. Don’t you use any economic incentive instruments, such as taxes, deposit-refund systems, etc.?
No… This does not depend upon us. There should be a proper state-regulated system established. And it does not exist here.
6. In your operations do you establish any partnerships with another company or NGO?
The company itself is a partnership. AVE Ungheni is an Austrian and Moldovan enterprise, the public-private partnership with the City Hall of Ungheni.
7. If you sort the municipal waste, do you also recycle it?
No, we have established cooperation with recycling companies abroad. As there is no recycling in Moldova, most of the waste we dispose to landfill sites, and plastic, paper and cardboard are exported to other countries, where it is recycled by our partners. For instance, PET is exported to Romania and treated there.
8. Is AVE Ungheni a Yes, this is the unique private waste management enterprise in the city
1 The interview was possible due to collaboration with the social movement “Hai, Moldova!” and with financial support from The Explorers Club Exploration Fund.
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single waste management company in Ungheni?
of Ungheni.
9. How do you think, will there be a recycling system established in Moldova soon?
The amount of waste in Moldova is not big enough to give incentive for a recycling company to come to the country. Therefore I believe there will not be any recycling here for the next ten years.
10. Then what can and should we do to make citizens practice proper waste management?
People should be pushed by the law. There should be proper waste management legislation enforced. Man is a lazy being, he needs to be directed in the right way by such means as legislation, fees, taxes, etc. And, of course, through education.
11. Do you consider an NGO such as “Hai, Moldova!” can do something about it?
Well… The girls from “Hai, Moldova!” approached me last year, and we tried to do some cooperation together. But then it all stopped… In general, I remained disappointed regarding “Hai, Moldova!”. They collected 6,000… 7,000 tons of waste… compared to the enormous amount that is generated nowadays. And we collect this amount in just one day.
12. But “Hai, Moldova!” is developing… So, are you open for possible future partnership with it?
Well… yes.
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Some Questions and Answers from the Survey by IMAS for the NGO “Hai, Moldova!”.
Details Sample Size 820 respondents (390 men, 430 women) 15 years and older from both
urban and rural areas Survey Mode Telephone interviews Organizer and Responsible Institute of Marketing and Polls IMAS-INC Chişinău
(www.imas-inc.md) Period 17.03.2012 – 21.03.2012 Place Republic of Moldova (except Transnistria)
Summary # Questions Answers
1. How is the problem of environment pollution dealt with in your area?
2. How do you see the
behaviour of Moldovan citizens with regard to environment protection?
3. When we discuss
environmental problems, do you consider that… ?
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4. To what extent is environment protection an important for… ? (0 – “Not important al all”; 10 – “Very important”)
5. To what extent are
you concerned about the following problems? (0 – “I do not care at all”; 10 – “I care very much”)
6. How much are you
interested in campaigns for environment protection?
7. Do you intend to
participate in the campaign “Hai, Moldova”! in 2012?
Source: IMAS (2012)
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Photo Gallery. Photo 1 – Locations of Different Waste Management Facilities at the Țânțăreni Landfill
Site Displayed at Its Entrance.
Taken by: Cucuietu (2012)
Photo 2 – Waste collection vehicle unloading its contents at the entrance to the Purcel
Mine “temporary” landfill.
Taken by: Iscenco (2012)
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Photo 3 – The functioning Purcel Mine landfill site near the village Bubueci, Moldova.
Taken by: Iscenco (2012)
Photo 4 – “Genesis” of a new illegal waste dump near the lake Vosmiorka outside
Chișinău, Moldova.
Taken by: Iscenco (2012)
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Photo 5 – MSW collection and sorting platform of the company AVE Ungheni SRL in the city of Ungheni, Moldova.
Taken by: Surdu (2012)
Photo 6 – Inside the container for waste separation in Ungheni, Moldova.
Taken by: Surdu (2012)
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Photo 7 – “Cage” for collecting PET with other types of waste in it.
Taken by: Surdu (2012)
Photo 8 – Participants of the “Hai, Chișinău!” campaign after the cleanup action
consuming food and drinks from plastic plates and cups.
Taken by: Iscenco (2012)
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Photo 9 – Inbicon Demonstration Plant for thermochemical treatment of biomass and agricultural waste in Kalundborg, Denmark.
Taken by: Iscenco (2011)
Photo 10 – Entrance to the Museum of Copenhagen and the temporary exhibition
“SKRALD!” (“TRASH!”) in Copenhagen, Denmark.
Taken by: Znaceni (2012)
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Photo 11 – Temporary “headquarters” of “Hai, Moldova!” with displays showing real-
time statistics on the number of participants and waste collected all over Moldova.
Taken by: Iscenco (2012)
Photo 12 – Orange collection point at the Roses Valley Park receiving 33 old mobile
phones for recycling.
Taken by: Iscenco (2012)
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Alexander Ișcenco
University of Copenhagen
www.ku.dk
Copenhagen, 2012
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