ReviewOptimizing Peri-URban Ecosystems (PURE) to re-couple urban-rural symbiosis
Graphical abstract
Introduction
Rapid urbanization, in many parts of the world, is driven by the desire for economic improvement coupled with the diminished employment opportunities in rural regions. As a consequence of unprecedented urbanization, globally more than 50% of the world population now live in cities (Grimm et al., 2008). The trade-off of urbanization is that less people now produce our food with an associated intensification of production, and agricultural land around metropolitan boundaries is being sealed over for buildings and transport infrastructure. Now, more than ever, the understanding and management of urban ecosystems have become an essential component of sustainable development.
A key feature of urban ecosystems is that nutrient stocks, carbon (C), nitrogen (N) and phosphorus (P), are being imported into urban ecosystem (through both natural and anthropogenic pathways). Significantly, these nutrients are not being returned to support primary production in rural/peri-urban environments from where they originated. For example, the food production required to sustain a city's population typically takes place in rural environments, but nutrient-rich wastes (resulting from food consumption) are emitted and processed in urban settings. Thus, reuse of urban nutrient wastes in rural and peri-urban environments is precluded from sustaining further production because: these wastes, and their associated nutrients, are often lost due to their discharge to water courses or incorporation in landfills; inadequate sewage collecting infrastructure and wastewater treatment approaches (that might realize suitable products to support soil improvement), and; a lack of mechanisms to return nutrients recovered from the urban environment to their point of origin. Overall, this cycle perpetuates a net gain of nutrients in the urban environment and a commensurate loss of nutrients from rural/peri-urban environments.
In order to redress nutrient losses in rural/peri-urban environments, and to sustain food-supply, chemical fertilizers are required to replenish this nutrient deficit. While this ‘fixes’ the soil nutrient problem the current use patterns of chemical fertilizers are unsustainable. Firstly, these practices result in the increased likelihood of nutrients being leached form soil into watercourses and causing damage to aquatic environments and additionally contributing to the rural to urban efflux of nutrients. Secondly, fertilizer production is heavily reliant upon with fossil fuels and as consequence production of inorganic fertilizers has a large carbon-footprint.
Section snippets
The concept of Peri-URban Ecosystems (PURE)
If we are to realize global sustainability goals (inter alia: sustainable cities and communities; responsible consumption and production; good health and well-being; clean water and sanitation, and to protect and conserve life on land and below water) (UN, 2012) then the inherent conflicts between urbanization, food security and environmental sustainability have to be resolved in the longer term. One of the focal points related to rapid urbanization will be a sustainable food system for city
Defining the common framework of PURE
Defining and sustaining the PURE for urban-rural symbiosis requires outlining a common, integrating framework of quantitative analysis that encompasses the considerable structural and functional differences encountered across the rural-urban transition zone. We propose to define integrating systems concepts for the reconnecting of rural and urban environments, through PURE management. One contributing framework is the concept of Earth's Critical Zone as a vertically integrated system that links
The dynamics of PURE
To understand the dynamics of PURE, the transitions and the services that humans require in an urban setting needs to be understood. In this regard, the seminal manuscript of Clements (1936) provides a suitable scaffold to draw analogy between climax states in the natural world (in Clements' case the vegetation of North America) and climax states associated with urbanization (Clements, 1936). With regards to the latter the inherent managed development of urbanization within the rural-urban
Managing PURE
Two aspects are of particular relevance to the management of PURE. Firstly, the intrinsic limitations of the waste flows themselves, and, secondly, the prevailing condition of the environment to which these flows are to be redirected. For example, in Beijing, 5374 t and 849 t of P in total were, respectively, consumed by urban and rural residents, in 2008 (Qiao et al., 2011). The largest outflow of P through food consumption in the city is discharge to waste water treatment plants (WWTPs),
Concluding remarks
Globally, the urbanization pace is not going to slow down. In China, for example, an unprecedented migration of people from rural to urban environments has taken place over the last 20 years. The urbanization of China's population is set to continue, and indeed intensify, with 250 million rural people being projected to migrate to urban centers by 2025. When set alongside current populations of, for example, New York (8.5 million), London (8.5 million) and Tokyo (13 million) such a figure is
Acknowledgments
This work was supported by the National Natural Science Foundation of China (41571130063), the Strategic Priority Research Program of Chinese Academy of Sciences (XDB15020302 and XDB15020402) and the International Science & Technology Cooperation Program of China (2011DFB91710).
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