Regional water footprint evaluation in China: A case of Liaoning

https://doi.org/10.1016/j.scitotenv.2012年10月04日9 Get rights and content

Abstract

Water-related problems are currently second only to energy issues as threats to human society. North China is a region that is facing severe water scarcity problems. In order to provide appropriate water mitigation policies a regional study is completed. Under this circumstance, Liaoning Province, a typical heavy industrial province in north China is chosen as a case study region. The input–output analysis method is employed in order to evaluate the water footprint both from production and consumption perspectives. The results show that the total water footprint of Liaoning in 2007 was 7.30 billion m3, a 84.6% of internal water footprint and a 15.4% external water footprint. The water trade balance of Liaoning was 2.68 billion m3, indicating that Liaoning was a net water export region, although water shortages are becoming a more serious concern. The "Agriculture" and "Food and beverage production" sectors are found to have the highest water footprint, water intensity, water exports, and water trade balance. Based upon Liaoning realities policy implications and suggestions are made, including industrial and trade structure adjustment, application of water efficient technology and management measures, and appropriate capacity-building efforts. The methodology and findings may be useful for investigation of water footprints throughout various regions of the world.

Highlights

► Input–output analysis method was employed to evaluate regional water footprint. ► Mitigation policies for alleviating regional water shortage should consider both direct and indirect water consumption. ► Industrial structure optimization and trade structure changes are useful approaches to reduce regional water stress. ► Water efficiency can be improved through application of innovative water saving technologies.

Introduction

Issues related to water are listed by Nobel laureate Richard Smalley as second only to energy in serious problems that threaten humanity over the next 50 years (Mohanty, 2003, Smalley Institute, 2012). Water problems such as water scarcity, water pollution, water-related waste and water sanitation are only expected to become worse. In some poor Asian countries there is a severe scarcity of potable water. The World Health Organization (WHO, 2012) has shown that 1.1 billion people globally do not have access to clean water.
The water crisis can be traced to at least two reasons, one is supply-based, the other is demand-based. First is the limited supply of fresh water available for human consumption. Only about 2.5% of the world's 1.39 billion km3 of water is fresh water (Gleick and Palaniappan, 2010, Sivakumar, 2011). Not all of this fresh water can be used because it may be stored in glaciers, in permanent snow cover, or in deep groundwater that is practically inaccessible. Only 90,000 km3 of fresh water, approximately 0.007% of the total water and 0.26% of the fresh water, is available for human consumption (Sivakumar, 2011).
The second reason is demand-driven, which is due to the excessive consumption of water accompanying rapid economic development and population increase. Statistical data show that the global water consumption in the last century increased almost six-fold (Margaux, 2012), and the amount of per capita water use has decreased and will continue to decline (Sivakumar, 2011). In addition, water resource distribution is imbalanced. For example, while people living near the Great Lakes region of the US have excessive water resources, people in Saharan regions suffer greatly from water shortage.
China is one of 13 countries in the world classified as lacking adequate water resources (Geng et al., 2010a). China's per capita water resources rank 121st in the world, only a quarter of the world's average level (Ge et al., 2011). Recently, over the past few years, water-related crises in China have increased in both frequency and severity corresponding to rapid economic development and urbanization. Moreover, China's water resources are unevenly distributed. For instance, while supporting more than half of the country's total population, North China has only about 20% of the total water resources (Guan and Hubacek, 2007). The International Water Management Institute (IWMI) estimated that the north China will be water scarce by 2025 (Rijsberman, 2006).
Water scarcity has been studied by many researchers utilizing a variety of indicators such as the Falkenmark indicator (Falkenmark et al., 1989), the physical and economical scarcity indicators (Seckler, 1998), the water poverty index (Sullivan et al., 2003), and the water vulnerability index (Raskin et al., 1997). Water footprint analysis is a novel method and indicator for studying the water situation from the consumption perspective (Hoekstra and Chapagain, 2007, Aldaya et al., 2010, Velázquez et al., 2011). Water footprint analysis not only determines the water consumption situation and scarcity but can also reflect the embodied or virtual water in imports and exports. However, the application of such a method in China is still in its early stage, especially in North China where water shortage is severe. Thus, it is critical to conduct such a study so that appropriate water management policies can be raised by considering the local realities.
An objective of this paper is to fill this gap by assessing the water footprint in a north China province, Liaoning. Liaoning province was selected due to its representative nature on water shortage and water pollution. Another objective is to relay how these research outcomes can be used to provide policy implications to the local government so that they can alleviate water resource pressures. Liaoning Province, similar to other provinces and many emerging economy nations worldwide, is undergoing urbanization and industrialization. The insights from these findings will give policy makers in China and worldwide a tool and expectation of issues that will be facing many of their regions, especially regions with rapid urbanization and industrialization.
To achieve these objectives the remainder of this paper begins with an overview of water footprint related studies undertaken identifying relevant research literatures and setting the stage for this study. Detail on the research methodology is provided, including overview of the input–output based analysis framework and data collection process. We then present the case study results and provide policy implications. Finally, we draw research conclusions and identify limitations and future research directions.

Section snippets

An overview of water footprint related studies

The water footprint concept is closely linked with "virtual water" or "embedded water" approaches (Hoekstra and Chapagain, 2007). This concept was first introduced in 2002 as an analogy of the "ecological footprint" (Hoekstra and Hung, 2003). The water footprint is an indicator of direct and indirect freshwater use. Unlike the ecological footprint, the water footprint is a volumetric measure of water consumption and pollution. Different accounting perspectives have led to different water

Methodology

In this section we describe the water footprint analysis framework, some background on the case study region, and data collection and preparation.

Virtual water content in Liaoning

Virtual water content (VWC) reflects water consumption intensity in different industrial sectors. It includes direct and indirect water intensity. Fig. 1 presents the VWC values for different industrial sectors, in which "Agriculture" (sector No. 1) has the highest VWC value of 486 m3/104 RMB. The agriculture sector also has the highest direct water intensity with a figure of 370 m3/104 RMB, which is higher than the sum total direct water intensity of all other industrial sectors. The "Food and

Policy implications

This study provides a detailed and comprehensive understanding of Liaoning's water footprint, consumption quantities and patterns. These results provide policy implications for alleviating water concerns in Liaoning, but also provide evidence for broader policy implications. Similar to Liaoning, many regions in a number of countries and regions are facing significant water management issues due to limited supply, rising demand in all sectors and a lack of integrated planning. The development

Conclusions

China's rapid industrialization and urbanization require a significant amount of freshwater resources. However, due to imbalanced water resource distribution, north China is especially facing and will continue to face severe water limitations over the next several decades. To respond to future water scarcity in north China, a detailed analysis on regional water footprints is critical so that more appropriate water resource management policies can be prepared. This paper selected Liaoning as a

Acknowledgment

This study was sponsored by the Natural Science Foundation of China (71033004), the Ministry of Science and Technology (2011BAJ06B01, 2011DFA91810), the Chinese Academy of Sciences' "One Hundred Talent Program" (2008-318), and Ministry of Environment of Japan (E-1105, K113002).

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