Cities as Sustainable Ecosystems:
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| Hari Srinivas | |
| Concept Note Series E-143. |
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Abstract: A city must have adequate infrastructure and flexibility to support the needs of its population. As in the case of the global system as a whole, cities must not use resources faster than they can be replenished or substituted for, nor generate pollution faster than it can be assimilated. One of the guiding principles for the future will be to reform urban systems so that they mimic the metabolism of nature. Rather than devouring water, food, energy, and processed goods, and then belching out the remains as pollutants, the city could align its consumption with realistic needs, produce more of its own food and energy, and put much more of its waste to use. Looking at cities as sustainable ecosystems draws its inspiration from the cyclical ecosystems of nature itself. It is sensitive to global impacts of local consumption and production patterns, and takes an interdisciplinary and interlinked approach in developing its activities, outputs and partners. Developing cities as sustainable ecosystems requires a radical increase in the productivity of the resources it uses, and the goods and services it produces. This entails changes in both production, design and technology stretch the utility value of energy, minerals, water, and other natural resources. Closed-loop systems return every output harmlessly back to the ecosystem, or become an input to another process. This requires consumption and production systems that are modeled after the cyclical ecosystems of nature itself. |
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Keywords: Urban environmental management, Sustainable ecosystems, Urbanization, Ecological footprint, Urban metabolism, Sustainable development, Built environment, Environmental policy |
![]() "Today's concepts such as circular economy, urban metabolism, regenerative cities, and nature-based solutions all build upon the ecosystem perspective described in this paper." See ANNEX below for an exploration of these emerging concepts |
The concern and problems associated with the environment have placed such issues high on the agenda of many bilateral and multilateral meetings. The Earth Summit of 1992 in Rio de Janeiro managed to highlight and channel efforts in understanding and acting on environmental problems, making it a key issue to be tackled in trade and commerce, in economic and social development, and in science and technology. Subsequent summits and congresses the Social Summit and the Beijing Conference on Women in 1995, the City Summit/Habitat II in 1996, not to mention innumerable regional, national and local meetings all had the larger global environment as a key common denominator in its action plans.
More recently, the Post-2015 Agendas, including the SDGs, have further enhanced the criticality of environmental issues and the need for their integration in public policy making. When the Millennium Development Goals (MDGs) ended in 2015, the international community came together once again, under the auspices of the United Nations, to formulate a set development agenda for adoption beyond 2015. These agendas (which go beyond the SDGs themselves) collectively became known as the "Post-2015 Agendas". They include the SDGs, the UN Climate Change convention, Finance for Development Agenda, Sendai Framework on Disaster Risk Reduction, the Humanitarian Agenda, and the Habitat Agenda.
It is only in the last few decades that a better understanding of the effects of changing environments and ecosystems has been developed. Interconnectedness of these factors has forced particular attention on human lifestyles and living conditions that has a profound effect on its surroundings. Most, if not all, environmental problems that we currently face can be directly or indirectly traced back to the legacy of lifestyles that we are inheriting and leading as human beings. Nowhere is this more true that in concentrations of gregarious urban lifestyles that are becoming the option of choice for the majority of humanity.
By the turn of this century, we were witness to a ubiquitous scenario where more people opted to live in and around cities than in rural areas. In the following decades, this urban shift has only accelerated. Today, over 55% of the global population resides in urban areas - a figure projected by the United Nations to reach nearly 70% by 2050. This rapid transformation cements cities not just as demographic hubs, but as the primary arenas where the future of global environmental sustainability will be decided.
| The world's cities take up just two percent of the Earth's surface, yet account for roughly 78 percent of the carbon emissions from human activities, 76 percent of industrial wood use, and 60 percent of the water tapped for use by people. |
The result of this has been the explosive growth of urban areas, bringing with it a host of negative effects. Population concentration in increasingly smaller land masses has caused a drastic decline in the quality of living both in the residential and work fronts. Cities have, in effect, become a barometer of humankind's progress into the 21st century, whether this is an upward or downward trend. Such a scenario has had ripple effects on a variety of sectors such as education, health, labour/job markets, and economic activities.
The growth and effect of an urban area should be seen not only in terms of its immediate boundaries, but also in terms of the resources necessary to sustain its population. An illustrative example is that of the Greater London area. The land mass that generates the resources necessary to sustain the population of London, called the 'urban footprint,' is actually slightly less than the entire land area of UK! This illustrates the complex interrelationship and interdependence of urban areas and their surrounding hinterland.
For example, based on GDRC research, Japanese lifestyles generate a demand for approximately 6.25 global hectares (gha) of biologically productive land and sea per person to provide resources and absorb wastes. However, Japan's own ecosystems provide only about 1.88 gha per person, leaving an ecological deficit of 4.37 gha per person that must be met through imports or by drawing on global ecological resources.
The Greater Tokyo metropolitan region had an estimated population of 37.4 million in 2025. For Tokyo alone, this ecological deficit amounts to approximately 163.4 million global hectares, equivalent to about 4.3 times the total land area of Japan. If only Japan's habitable land is considered, excluding mountains, forests unsuitable for settlement, and inland water bodies, the deficit corresponds to roughly 13.4 times the country's habitable land area.
The effects of urban activities have in many cases outweighed the relative advantages of agglomeration and centrality that they have offered. Thus, along with the benefits of urbanization come environmental and social ills, including lack of access to drinking water and sanitation services, pollution and carbon emissions etc. A wide variety of urban problems can be observed, grouped under two broad contradictive classes, those associated with poverty and those associated with economic growth and affluence.
Burgeoning cities are expanding into fragile ecosystems ... Cities sometimes deplete nearby areas of water and firewood, rendering them less capable of supporting rural populations and thus adding to the pressures for urban migration. Air pollution already exceeds health standards in many megacities in developing countries. Sewage and industrial effluents are released into water-ways with minimal or no treatment, threatening human health and aquatic life. Some urban environmental problems such as access to safe drinking water improve with economic growth, while others tend to worsen.
Thus in the absence of policy reform, stronger institutions, and enlightened political leadership, economic and population growth in developing countries in the near term may lead to a deterioration of the urban environment, both physical and social. Stresses on the global environment from urban activities are also likely to accelerate. A major share of greenhouse gas emissions already comes from the use of fossil fuels in wealthy urban areas, especially in the developed countries.
While laws exist to effect interaction and participation between the various actors involved in urban growth processes, it is not adequately exercised both on the part of local governments (sufficient information was not provided), as well as other actors and citizens themselves (there was no commitment to participate). Information that is shared by the government is, in many cases, partial or selective. There has, however, been a growing awareness of environmental problems and its causes and effects.
With a gradual increase in the transparency and openness in the functional organization and operation of local governments, legislation on information disclosure has been receiving considerable importance. Basic understanding of environmental management of cities and the consequent needs of information for decision making processes has also improved. Community involvement becomes all the more critical when the shortcomings and weaknesses of local governments to effectively deal with the range of problems are taken into account. All this has necessitated a hard rethinking and reexamination of the intrinsic and symbiotic (negative and positive) relationships between human lifestyles and natural resources that is depended upon.

It is helpful therefore, to look at urban environments from three view points: the natural environment, the built environment and the socio-economic environment. Natural environments are essentially resources, processes and effects related to flora and fauna, human beings, minerals, water, land, air, etc. Built environments are resources, processes and effects related to buildings, housing, roads, railways, electricity, water supply, gas etc. The socio-economic environment includes resources, processes and effects related to human activities, education, health, arts and culture, economic and business activities, heritage - urban lifestyles in general. It is the intersection and overlay of these three dimensions that constitutes an 'urban environment'.
| Dimension | Core Resources Included | Primary Urban Process | Key Systemic Stresses |
|---|---|---|---|
| Natural | Flora, fauna, water tables, air sheds, minerals | Resource extraction, climate regulation | Pollution, resource depletion, habitat fragmentation |
| Built | Housing, transit networks, grids, civil infrastructure | Construction, energy distribution, logistics | Congestion, infrastructure decay, urban heat islands |
| Socio-Economic | Human capital, financial assets, cultural heritage | Migration, education, commerce, governance | Wealth disparity, health crises, loss of cultural identity |
Taking any one dimension at the exclusion of the other two, poses the inevitable danger of missing the forest for the trees - the interdependency and interdisciplinarity of the three dimensions have to be fully understood in the development of coherent and sustainable policies and programmes for the urban environment. This is particularly true with the multiplicity of actors and activities - there has been a growing realization that state agencies and activities are, but one part of a spectrum of agencies and activities that are involved in the urban environment.
Interaction between the different actors at different levels of urban growth processes and cycles becomes critical to respond to the increasingly complex policy and investment choices that urban communities face. There are many key points that arise in support of a sound urban environmental policy. The concept of sustainable development ought to take into account the needs of future generations in decisions on how and whether to use resources and apply technologies, through policies, investments and development plans.
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One of the guiding principles for the future will be to reform urban systems so that they mimic the metabolism of nature.
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To systematically track and manage this urban metabolism, planners can utilize the MEWW (Materials, Energy, Water, and Waste) framework. This diagnostic approach treats a city as a living organism by auditing its four critical resource flows:
| MEWW Pillar | Primary Urban Input (Resources) | Metabolic Transformation (Processes) | Systemic Output (Effects) |
|---|---|---|---|
| Materials | Land, minerals, metals, timber, intermediary products, construction aggregates, recyclable materials. | Infrastructure construction, manufacturing, asset maintenance, building demolition, material sorting. | Built environment expansion, physical waste generation, urban density, resource depletion. |
| Energy | Sunlight, electricity, fossil fuels (coal, oil, gas), biofuels, regional grid power. | Transit logistics, residential heating/cooling, commercial operations, manufacturing activities. | Carbon emissions, thermal pollution, urban heat island effects, economic productivity. |
| Water | Freshwater bodies, regional aquifers, rainwater harvesting streams, imported municipal water. | Domestic consumption, industrial cooling, sanitation, wastewater transit, urban landscape irrigation. | Sewage generation, groundwater drawdown, aquatic ecosystem stress, runoff pollution. |
| Waste | Post-consumer refuse, organic/food scrap, hazardous effluents, manufacturing industrial byproducts. | Recycling sorting loops, organic composting, waste-to-energy incineration, landfill management. | Circular resource recovery, soil/air pollution mitigation, reduction in landfill dependencies. |
By balancing these four interconnected pillars, the MEWW framework provides municipalities with a concrete, measurable roadmap to convert linear urban supply chains into circular, self-sustaining loops.
Environmental policies have to be based on an understanding of the causes of environmental degradation and of the environmental impacts and cost-effectiveness of solutions, as well as the uncertainties associated with it. Policies should also contribute to greater public understanding of environmental issues through more open access to information and decision-making process. Operationalizing environmental policies, therefore, require the integration of many interrelated economic, environmental, social and cultural factors.
Consolidating the ideas and issues together is the ecosystem approach. An urban ecosystem brings together the resources, processes and products into a coherent system that exchanges and makes use of byproducts and/or energy - aiming towards the reduction in the use of virgin materials as resource inputs; reduction in pollution; increased energy efficiency leading to reduced energy use in the system as a whole; reduction in the volume of waste products requiring disposal (with the added benefit of preventing disposal-related pollution); and increase in the amount and types of process outputs that have market value.
| For a defined outcome ... | ||
Issues |
More sustainable |
Less sustainable |
| Absolute impacts (species loss, emissions to air, water or soil (incl. noise, dust, odour) | Less (aim for zero) | More |
| Absolute resource use (finite & renewable resources) | Less (aim for zero) | More |
| Intensity / efficiency of resource use and impacts | Less (energy, water, soil etc, or emissions and other impacts) used per $ GNP produced, or per unit of production | More |
| Energy / material throughput rate | Slower. Ambient temperature and pressure operation | Faster, less throughput (even if process generates energy) |
| Energy / material cycle | Shorter cycle3, more recycled | Longer cycle3, less recycled |
| Design life / durability | Longer / more durable | Shorter / less durable |
| Biodiversity / ecosystem stability | Increases / stabilises | Decreases / destabilises |
| Price of product / service | Reflects all known costs / benefits (internalises real costs of production / disposal | Distorted (affected by subsidies, non-compliance, cost externalisation) |
| Resources price progressivity | Progressive and inverse to known reserves2 | Flat or regressive |
| Fiscal signal to production - prices, taxes and charges | Rewards reduced impact, resource conservation, efficiency, feeding back incentive to product designers to design waste and toxicity out of the system; passes on public savings resulting from private choice, taxes undesirable activity (eg. pollution, congestion), taxes specifics. | Ignores or punishes reduced impact, rewards waste, hides real costs of private choices in general taxation eg. fixed annual charges, underpriced infrastructure charges, hides diseconomies of scale, no incentive to design waste and toxicity out of the system. |
| Subsidy | Less. If given, make transparent. Pay in cash not kind | More. Hidden as underpriced water, fuel, etc. |
| Market1 competition | Fair and open market access4 | Barriers to market entry |
| Market1 information about products and services, and relevant costs | More and better quality, more accessible, more timely, labels stating the efficiency, running cost, design life, origin and toxicity, real time usage metres | Less, lower quality, less accessible, delayed usage and cost information (eg. quarterly energy bills) |
| Scale | Smaller | Larger |
| Decision making | Devolves downward | Concentrates and centralises |
| Diversity in society, social, economic and engineering processes | Increases, decentralised systems, circular flows | Diminishes, centralised systems, linear flows |
| Equity | Inter and intra generational | Decreases |
| Planning framework | Long term | Short term |
| Materials flow | Maximum separation | Co-mingled |
| Basis of product use | Lease / share / hire / service | Personal ownership |
| Source: | Adopted from comments by Doug Yuille, Environmental Policy Adviser, Lord Mayor's Office, Brisbane, Australia. |
Notes: |
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A city must have adequate infrastructure and flexibility to support the needs of its population, and the needs of the ecosystem as a whole. As in the case of the global system as a whole, cities must not use resources faster than they can be replenished or substituted for, nor generate pollution faster than it can be assimilated. One of the guiding principles for the future will be to reform urban systems so that they mimic the metabolism of nature. Rather than devouring water, food, energy, and processed goods, and then belching out the remains as pollutants, the city could align its consumption with realistic needs, produce more of its own food and energy, and put much more of its waste to use.
Looking at cities as sustainable ecosystems draws its inspiration from the cyclical ecosystems of nature itself. It is sensitive to global impacts of local consumption and production patterns, and takes an interdisciplinary and interlinked approach in developing its activities, outputs and partners.
Developing cities as sustainable ecosystems requires a radical increase in the productivity of the resources it uses, and the goods and services it produces. This entails changes in both production, design and technology stretch the utility value of energy, minerals, water, and other natural resources. Closed-loop systems return every output harmlessly back to the ecosystem, or become an input to another process. This requires consumption and production systems that are modeled after the cyclical ecosystems of nature itself.
This clearly needs an objective, multidisciplinary study of urban and economic systems and their linkages with fundamental natural systems. Research on energy supply and use, new materials, new technologies and technological systems, and other relevant issues is critical for a better understanding of the issues involved.
In a broader sense, the ecosystem approach should be applied at all levels of resource consumption in a city - from building design and construction and its use, to macro scale issues of urban planning and development, urban management, network and social infrastructure (roads, electricity, gas, telecommunications, schools, hospitals etc.).
The urban ecosystem approach raises several critical needs:
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Emerging Needs (2025 and beyond) The ecosystems approach will have to to be contextualized within a number of other emerging topics as well:
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