Enda Preceup
Research Component
Efficient Management Practices in Disposal of Solid Waste in Asian Urban Environment
A regional review
Contents
1. INTRODUCTION
1.1 Global Agenda for Urban Environment
1.1.1 Better environmental information and technical expertise
1.1.2 Better environmental strategies and decision-making
1.1.3 More effective implementation of environmental strategies
1.1.4 Enhanced institutional and participatory capacities
1.1.5 More effective use of scarce resources for capacity-building and change
1.2 International Support Programmes
1.3 Composition of Waste
1.3.1 International Differences in Solid Waste Parameters
1.3.2 Composition and quantities of solid wastes in select Asian cities.
1.4 Urban environment management dimensions
1.5 Solid Waste Management Cycle
2.1.1 Industrial waste
2.1.2 Domestic and vegetable market waste
2.1.3 Commercial market waste
2.1.4 Hospital waste
2.1.5 Miscellaneous sources
2.2 Type of waste
2.2.1 Liquid/solid
2.2.2 Degradable/non-degradable
2.2.3 Reusable/non-reusable
2.2.4 Recyclable or non recyclable
2.3 Monitoring disposal of waste
3. COLLECTION AND TRANSFER OF WASTE
3.1.1 House to house collection
3.1.2 Block to Block or Kerbside collection
3.1.3 Garbage bins to dumping grounds
3.2 Salvage
3.2.1 Retrieval Systems
3.2.2 Recyclable materials collected by informal sector waste-pickers from garbage dumps
3.3 Resale/Reuse/Recycle
3.3.1 Recovery and Reuse
3.3.1.1 Benefits of recycling
3.3.2 Redemption Centres
3.3.3 Salvage Dealers
4.1 Disposal Methods
4.1.1 Land fill
4.1.1.1 Pit method
4.1.1.2 Area method
4.1.1.3 Ramp method
4.1.2 Incineration method of garbage disposal
4.1.3 Compaction or compression of refuse : Volume reduction process of disposal
4.1.4 Pyrolysis
4.1.5 Bio-gas
4.1.5.1 Thermophilic bio-digestion
4.1.5.2 Bio-methanation
4.1.6 Pelletisation
4.1.7 Composting
4.1.7.1 Windrow process
4.1.7.2 Close cell process
4.1.8 Uses of Compost
4.1.9 Vermiculture
4.1.10 Health impacts
5.1 Policy issues
5.1.1.1 Appropriate disposal method
5.1.2 Policies governing informal sector with a special consideration for poverty groups
5.1.2.1 Gender sensitisation
5.1.3 Legal and regulatory provisions
5.2 Planning issues
5.2.1 Decentralisation and micro-planning
5.2.2 Finance for Solid Waste Management
5.2.3 Marketing
5.3 Organisational issues
5.3.1 Efficiency in operations
5.3.2 Unionisation and Co-operativisation
5.4 Partnership issues
5.4.1 Privatisation and cost-sharing
5.4.2 Role of NGOs
5.4.3 Networking
5.4.4 Community education
5.5 Conclusion
References
Annexure I : Networks as Actors in Urban Environment Improvement in Asia 59
Case studies used in the document
Box 1 : Colombo Metropolitan area, Sri Lanka 30
Box 2 : Ayala Foundation, Manila, Philippines 32
Box 3 : SEWA, Ahmedabad, India 35
Box 4 : Surat Municipal Corporation, India 38
Box 5 : Din Daeng Mechanical Compost Plant, Bangkok, Thailand 39
Box 6 : Singapore city 41
Box 7 : Kuala Lumpur 42
Box 8 : GRASP, Pune, India 44
Box 9 : Pimpri Chinchwad Municipal Corporation, India 47
Box 10 : Binh Hung Hoa Project, HCM city, Enda Vietnam - Preceup 50
Box 11: Orangi Pilot Project, Karachi, Pakistan 52
Box 12 : Metro Manila Women’s garbage recycling programme, Philippines 54
The objectives of economic development and poverty alleviation, as they exist today, seem to be conflicting with environmental considerations, resulting in the absence of effective environmental management in the cities. Cities are full of contradictions for human development, resulting in centres of "growth and wealth" on the one hand and "need and poverty" on the other. Poverty to a large extent is linked with the degraded environment and the rapid population growth. But there is a tendency to overemphasise the second factor, thereby undermining the consequences of degraded environment, although the impact of local environments are both visible and dangerous.
Environmental degradation also has long term effects on resources and human potentials, thereby threatening the overall eco-system. On the information front, there is an absence of the most essential information for decision making and for execution of appropriate development programmes which would incorporate environment - security-poverty system. This would also have implications for the opportunity for participation of the poor in the general socio-political and economic system. A careful analysis of the living conditions of the poor and their perceptions on the daily environment, coupled with their creative responses, would contribute to our understanding the major source of progress.
Today’s cities are duel systems providing many spaces for self-management and planning on the one hand, and restraining popular initiatives on the other. In view of the inadequacies of bureaucratic planning and technocratic management models, the prospects of strengthening popular autonomy and self expression will have to be effectively re-enforced and integrated for economic independence and political democracy.
1.1 Global Agenda for Urban Environment
Global Agenda for Urban Environment of the United Nations Conference of Human Settlements (UNCHS), have underlined the principles governing the process of Urban Environment Planning and Management (EPM). These have been grouped under five main headings :
· Better environmental information and technical expertise
· Better environmental strategies and decision-making
· More effective implementation of environmental strategies
· Enhanced institutional and participatory capacities
· More effective use of scarce resources for capacity-building and change
1.1.1 Better environmental information and technical expertise
· Preparing basic environmental management information
· Involving stakeholders
· Setting priorities
· Clarifying priority issues
1.1.2 Better environmental strategies and decision-making
· Clarifying issue-specific policy options
· Considering implementation options and resources
· Building broad-based consensus on issue-specific objectives and strategies
· Coordinating environmental and urban development strategies
1.1.3 More effective implementation of environmental strategies
· Applying the full range of implementation capabilities
· Agreeing on action plans for implementation
· Developing packages of mutually supportive interventions
· Consolidating political support and mobilisation of resources
1.1.4 Enhanced institutional and participatory capacities
· Strengthening system- wide capacities for EPM
· Institutionalising broad-based participatory approaches to decision-making
· Strengthening cross-sectoral and inter-institutional coordination
· Monitoring, evaluating, and adjusting the EPM system
1.1.5 More effective use of scarce resources for capacity-building and change
· Utilising special opportunities
· Applying specific leveraging strategies
· Networking among cities
· Strategic use of external support
1.2 International Support Programmes
International support programmes of United Nations agencies, other multilateral organisations, bilateral institutions, NGOs, and of other international organisations illustrate strategies for co-operating with and supporting cities in implementing their urban environment agenda. These programmes include :
· Sustainable Cities Programme (SCP) - UNCHS (Habitat), UNEP, Nairobi
· Sustainable Cities Initiative - USAID, Washington
· Urban Environmental Training Programme - GTZ, Germany
· International Centre for Sustainable Cities (ICSC) - Canada
· Local Initiative Facility for the Urban Environment (LIFE) - UNDP
· Metropolitan Environmental Improvement Programme (MEIP) - WB, UNDP
· Urban Management Programme, Environment (UMP/E) - UNCHS, WB, UNDP
· Citynet - Yokohama, Japan
· Urban Management Programme, Latin America and Caribbean (UMP/LAC)
· Baltic Sustainable Cities Programme - Union of Baltic Cities (UBC)
· Awareness and Preparedness for Emergencies at Local Level (APELL) - UNEP, Paris
· Public, Private, Partnership Programme (PPPP) - UNDP, New York
· Healthy Cities Project - WHO, Geneva
· International Environmental Technology Centre - UNEP, Osaka
· Cities Feeding People - IDRC, Canada
· Integrity in Urban Governance Programme - Transparency International (TI), Berlin
· Global Environmental Monitoring System, Air (GEMS-air) - UNEP, Nairobi
· Capacity Building for the Urban Environment - IHS, Netherlands
· Peri-Urban Interface Research (PUI) - NRI, ODA, United Kingdom
· Local Agenda 21 - ICLEI
(Reference 17)
It is estimated that the global burden of Municipal Solid Waste (MSW) amounted to 1.3 billion metric tonnes in 1990, or two-thirds of a kilogram of waste per person per day. It is widely accepted that industrialised countries account for a disproportionately high share of the world’s waste relative to their share of the world’s population. Analyses across countries and over time reveal that the generation of MSW per capita does not vary with population size among countries with comparable per capital income. In the more wasteful economics, there are higher expectations for waste services, but insufficient attention to waste reduction and recycling. Understanding of the dynamics and the costs of MSW management needs to be increased among the public and also among administration and politicians.
Studies on solid waste management have recorded the composition of solid waste in major Asian cities. SWM practices in Asia differ from those in the West, in that the waste produced in Asia is largely recycled owing to the fact that it is no ‘wegwerfgesellschaft’ or a society that believes in using and throwing.
1.3.1 International Differences in Solid Waste Parameters
|
UK 1975 |
Iran 1973 |
Calcutta, India 1970 |
||
|
Screenings |
% |
20 |
27 |
42 |
|
Vegetables etc. |
% |
21 |
51 |
16 |
|
Paper |
% |
27 |
9 |
3 |
|
Metals |
% |
8 |
2 |
0.7 |
|
Glass |
% |
10 |
2 |
7 |
|
Plastic |
% |
3 |
2 |
0.6 |
|
Textiles, misc. |
% |
11 |
7 |
9 |
|
Weight Density Volume |
gm/cap. Day kg/m3 1/cap. day |
900 150 6 |
290 250 1.2 |
510 530 1.0 |
(Reference 5)
Paper and plastic contents are generally higher in cities like Tokyo and Singapore. In cities like Beijing and Shanghai, the ash/soil content is very high due to the burning of coal and space heating during the cold seasons whereas the proportion of papers, textiles, and the light materials is very low, due to recovery and recycling.
In general, the South Asian countries have high percentages of organic and inert matter in their disposed residues, whereas the northern and central Asian regions have more synthetic and combustible materials, metals, glass, and toxic goods such as batteries.
Most of the reports on MSW for cities in south Asia note waste generation rates ranging from less than 0.5 kg/capita/day to 0.8 kg/capita/day; the central area reports show a higher generation rate of more than 0.75 kg/capita/day. The composition of waste for select cities of Asia is given below.
1.3.2 Composition and quantities of solid wastes in select Asian cities.
|
Bombay |
Colombo |
Manila |
Bangkok |
Kuala Lumpur |
Singapore |
Beijing |
Shanghai |
Tokyo |
|
|
Area (Km2) |
466.35 |
36.6 |
636 |
1,568.74 |
43 |
618.1 |
16,807 |
6340.5 |
599.73 |
|
Population (103) |
8,243(81) |
586 (86) |
7561(88) |
5,609(87) |
1036(80) |
2613(87) |
9880(87) |
12323(8) |
8354(87) |
|
Refuse Composition Moisture |
40 |
42.6 |
59.1 |
50.2 |
53.4 |
36.4 |
40.9 |
47.9 |
|
|
Combustible |
22 |
33.8 |
37.7 |
41.4 |
32.8 |
15.4 |
4.2 |
45.0 |
|
|
Incombustible |
38 |
23.6 |
5.2 |
8.4 |
13.8 |
48.2 |
54.9 |
7.1 |
|
|
Physical composition Paper |
10 |
14.5 |
13.9 |
11.7 |
28.3 |
7.8 |
2.6 |
42.0 |
|
|
Glass |
0.2 |
2.7 |
2.0 |
2.5 |
5.7 |
2.4 |
1.3 |
1.2 |
|
|
Metal |
0.2 |
4.9 |
1.8 |
6.4 |
4.8 |
1.1 |
2.9 |
1.2 |
|
|
Plastics |
2 |
7.5 |
11.0 |
7.0 |
11.8 |
2.8 |
1.6 |
8.5 |
|
|
Textiles |
3.6 |
1.3 |
6.9 |
1.3 |
3.0 |
1.4 |
0.3 |
3.8 |
|
|
Wood/Grass |
20 |
7.7 |
14.9 |
6.5 |
44.4 |
2.6 |
7.1 |
4.7 |
|
|
Ash/Soil |
20 |
31.8 |
36.5 |
63.7 |
29.2 |
31.5 |
32.9 |
||
|
Food waste |
38 |
6.0 |
12.6 |
0.9 |
2.0 |
48.2 |
51.1 |
0.1 |
|
|
Others |
62 |
23.6 |
0.4 |
0.0 |
4.5 |
1.6 |
5.6 |
||
|
Refuse density |
0.325ton/m3 |
0.33 |
0.33 |
0.27 |
0.21 |
0476ton/m3 |
0.5 |
0.185 |
|
|
L. Calorific value (Kcal/Kg) |
800-1,000 |
1,468 |
1130 |
750 |
1388 |
500-600 |
700.800 |
1898 |
|
|
Waste generation 103 ton/year Kg/capita/day |
1,1150 0.5-0.6 |
1,380 0.5 |
1800 0.88 |
730 1.29 |
1873 0.98 |
3580 1.59 |
2256 0.869 |
4491 0.54 |
|
|
Waste collection (103ton/year) |
1,1150 |
1,140 |
1533 |
730 |
943 |
2983 |
2256 |
3417 |
(Reference 3)
Developing countries, especially in Asia, are being transformed into a world of cities and towns. Recent projections indicate that more than half the population in these developing countries will be living in urban areas by the year 2020. Urban population growth has been fueled by migration from rural areas for prospects of higher incomes that have largely been realised. Yet cities have not been able to provide a better quality of life despite the relatively higher incomes of urban populations. With respect to drinking water, population in the urban areas do not have direct access to potable water, and even those having access often are not sure about the quality. Very similar problems are encountered in other areas of basic urban services such as sanitation, collection and disposal of solid wastes, air and water quality, transport as well as education and health services.
The lifestyles in an urban environment are basically influenced by the level of urbanisation, industrialisation and degree of consumerism as well as the capacity of the communities as reflected through the culture, administrative and institutional capabilities and extent of mobilisation for a collective response. Today’s urban environment is characterised by the problems which have global characteristics on the one hand, and possibilities of local solutions on the other. The efficiency of these local solutions have been well established in the given context. However, the effectiveness of their global application or possibilities for scaling up of these applications, have yet to be established.
Although, one can list a number of environmental issues that need immediate attention, the concerns of Preceup, as reflected in the exercises undertaken during the last few years, both in terms of research and action, highlight four major dimensions. These major dimensions of urban environment, that is, air, water, solid waste, and sanitation, which affect the lifestyle, are influenced directly by the manner in which these dimensions are managed. For the purpose of analysis, these dimensions have been elaborated in terms of the source, the impacts, the management process, the technologies, and the actors involved highlighting certain common characteristics and distinctions. Since solid waste management represents a more complex and comprehensive dimension, this document tries to explore further details with regard to the various stages in the solid waste management cycle. A cursory glance at this cycle indicates the possibility of universal application to the other dimensions of urban environment.
1.4 Urban environment management dimensions
|
Dimension |
Source |
Impacts |
Management Processes |
Technologies |
Actors |
|
Air |
Industries, domestic fuel, automobiles |
Health, flora and fauna, global warming |
Cost-sharing, partnership, administrative control, penal actions, advocacy |
Pollution control norms, scrubbers, absorbers, smokeless stoves, |
Industries, administration, monitoring agencies, NGOs, community |
|
Water |
Industries, domestic waste |
Health, aqua-marine life, economic |
Cost-sharing, partnership, administrative control, penal actions, co-operativisation, advocacy |
Effluent treatment plants, chlorination, filteration, sedimentation |
Industries, administration, monitoring agencies, NGOs, CBOs, community |
|
Solid waste |
Industries, markets, domestic waste, institutional |
Land quality, health, economic environment, |
Cost-sharing, community management, partnership, administrative control, penal actions, decentralised responsibility, advocacy, membership, unionisation, co-operativisation, privatisation, community participation |
Land fill, incinerators, bio-gas, composting, reuse, recycling, vermiculture, pelletisation, pyrolisation |
Industries, administration, NGOs, CBOs, informal sector, families and communities |
|
Sanitation |
Domestic, institutional |
Health and environment |
Cost-sharing, partnership, administrative control, penal actions, decentralised responsibility, co-operativisation, advocacy, privatisation, community participation |
Underground sewer system, open drainage system, bio-gas, composting, septic tanks, aereated lagoons |
Administration, NGOs, CBOs, families and communities |
1.5 Solid Waste Management Cycle
|
Lifestyle urbanisation, industrialisation, consumerism |
||
|
Source (Domestic, market, industries, institutional, etc) |
Product (land reclamation, compost, energy, cooking gas, cheaper goods, etc) |
|
|
Collection (Salvage, sorting, collection methods, etc) |
Processing (composting, compacting, vermiculture, landfill, recycling, incinerators etc) |
|
|
Transfer (dumpers, compactors, etc) |