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Frontiers of Earth Science

ISSN 2095-0195

ISSN 2095-0209(Online)

CN 11-5982/P

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2018 Impact Factor: 1.205

Front. Earth Sci.    2020, Vol. 14 Issue (2) : 268-285    https://doi.org/10.1007/s11707-019-0795-3
RESEARCH ARTICLE
Toward a socio-political approach to water management: successes and limitations of IWRM programs in rural north-western China
KuoRay MAO1(), Qian ZHANG2, Yongji XUE3, Nefratiri WEEKS1
1. Department of Sociology, Colorado State University, Fort Collins, CO 80523, USA
2. Institute of Sociology, Chinese Academy of Social Sciences, Beijing 100001, China
3. School of Economies & Management, Beijing Forestry University, Beijing 100083, China
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Abstract

In rural north-western China, the tension between economic growth and ecological crises demonstrates the limitations of dominant top-down approaches to water management. In the 1990s, the Chinese government adopted the Integrated Water Resources Management (IWRM) approach to combat the degradation of water and ecological systems throughout its rural regions. While the approach has had some success at reducing desertification, water shortage, and ecological deterioration, there are important limitations and obstacles that continue to impede optimum outcomes in water management. As the current IWRM approach is instituted through a top-down centralized bureaucratic structure, it often fails to address the socio-political context in which water management is embedded and therefore lacks a complete treatment of how power is embedded in the bureaucracy and how it articulates through economic growth imperatives set by the Chinese state. The approach has relied on infrastructure heavy and technocratic solutions to govern water demand, which has worked to undermine the focus on integration and public participation. Finally, the historical process through which water management mechanisms have been instituted are fraught with bureaucratic fragmentation and processes of centralization that work against some of its primary goals such as reducing uncertainty and risk in water management systems. This article reveals the historical, social, political, and economic processes behind these shortcomings in water management in rural north-western China by focusing on the limitations of a top-down approach that rely on infrastructure, technology, and quantification, and thereby advances a more holistic, socio-political perspective for water management that considers the state-society dynamics inherent in water governance in rural China.

Keywords integrated water resources management      top-down implementation      inland river basin      water rights      China     
Corresponding Author(s): KuoRay MAO   
Online First Date: 31 March 2020    Issue Date: 21 July 2020
 Cite this article:   
KuoRay MAO,Qian ZHANG,Yongji XUE, et al. Toward a socio-political approach to water management: successes and limitations of IWRM programs in rural north-western China[J]. Front. Earth Sci., 2020, 14(2): 268-285.
 URL:  
https://academic.hep.com.cn/fesci/EN/10.1007/s11707-019-0795-3
https://academic.hep.com.cn/fesci/EN/Y2020/V14/I2/268
Fig.1  Background of Interviewees.
Major themes Sample questions
Changes in agricultural production Has the IWRM program affected how you farm the land?
In what ways has the IWRM program affected the patterns of water consumption in your village?
How much money have you invested in water-saving infrastructure such as horticulture greenhouses and drip-irrigation?
How has the IWRM program shaped the allocation of land resources and the scale of agricultural production in your village?
How have the application of technology and subsidies affected the dominant ways of production in your village?
How have out-migration, capitalization, and stratification shaped the implementation of the IWRM program?
Environmental awareness and conservation of natural resources What have been the environmental and economic benefits of the IWRM program in Minqin?
Have there been any changes in the environment in vicinity of your village/township?
In what ways has the IWRM program changed how you utilize water and land resources in your household and village?
Would you be willing to change how you utilize water and land resources after the completion of the IWRM program?
How successful is the IWRM program in Minqin?
Opportunities & obstacles of IWRM implementation (grassroots cadres & villagers) How was the IWRM program implemented in Minqin?
What were the major obstacles for the state’s drive to reduce cultivation areas?
How did the local government promote the construction of horticulture green houses and drip irrigation infrastructure?
In what ways has the local government ensured accountability of program outcomes?
What have been the main obstacles to the sustainability of the IWRM program? How has the local government addressed these obstacles?
How have the central and local governments shared the cost of program implementation in Minqin?
Public participation & decision making
(grassroots cadres & villagers)
How have the county government, irrigation districts, and townships determined allocation of water resources?
How have the Water Users’ Associations operated in Minqin?
How have the construction of metered wells and the expansion of water-saving infrastructure shaped decision-making at the grassroots level?
What have been the major mechanisms to ensure public participation in the formulation of program goals and the implementation process?
How have the restrictive goals of the IWRM program shaped the implementation process?
Tab.1  Summary of interview questions used in Minqin County
Watershed Hei River Tarim River Shiyang River Shule river
Province Gansu Xinjiang Gansu Gansu
River basin organizations Hei River Basin Management Bureau, Yellow River Conservancy Commission (for surface water), MWR 1999 Tarim River Basin Management Bureau, Xinjiang Uyghur Autonomous Region Water Resources Bureau
1997 (reformed in 2011)
Shiyang River Basin Management Bureau, Gansu Provincial Water Resources Bureau 2002 Shule River Basin Management Bureau, Gansu Provincial Water Resources Bureau 2004
Plan examined Short-term Governance Plan of Hei River Watershed
(The next phase of the Hei River IWRM program is still being reviewed by MWR as of October 2018)
Short-term Governance Plan of Tarim River Watershed
(The next phase of the Tarim River IWRM program is still being reviewed by MWR as of October 2018)
Key Governance Plan of Shiyang River Watershed Integrated Plan on Rational Water Resource Use and Ecological Conservation of Dunhuang
(The IWRM of Dunhuang also includes the Dong River Watershed)
Plan duration 2002–2011 2001–2017 2007–2020 2011–2020
investment (billion yuan)- 2.35 10.739 4.749 4.722
Water-saving irrigation and diversion projects Y Y Y Y
Wells and cultivated land reduction Y (Implemented by Zhangye Prefecture Water Resources Bureau) Y Y Y (Implemented by Guazhou County Water Affairs Bureau)
Crop adjustments Y Y Y
Pollution control Y Y Y
Ecological restoration Y Y Y Y
Ecological migration Y Y
Administrative chief Responsibility system Y Y Y Y
Local watershed regulations Y Y Y Y
Water rights allocation Y Y Y
Water resources fees Y Y Y Y
Water users’ association Y Y Y Y
Tab.2  The IWRM programs of Tarim, Shule, Hei and Shiyang watersheds in Western China
Fig.2  Governance structure, expected outcomes & administrative measures of IWRM programs in north-western China.
Watersheds Hei River Tarim River Shiyang River Shule River
Dam construction & expansion Huangzangsi Water Control Project Expanding eight small reservoirs in the Watersheds Expanding and heightening Hongyashan Dam from 99 million to 148 million m3 Building Changma Reservoir
Water saving irrigation Implemented on 0.46 million mu cultivated lands, but the amount of water use increased by 20 million m3 for 0.35 million mu new cultivated land Implemented on 0.44 million mu cultivated land with water saving irrigation, including 8160 km seepage prevention channels 436.23 km of anti-seepage canals, 18,833 hectares of drip irrigated fields, and 1873 hectares of greenhouses Implemented on 1.00 million mu cultivated lands, including 405 km seepage prevention channel
Diversion structures Langxin Mountain Water Diversion Hub, Anci River Water Diversion Hub Patamu Diversion Hub Jintaichuan Diversion Project Phase II Extension Haleteng River Diversion Project
Tab.3  Flow-control infrastructure and water saving irrigation implemented by the IWRM programs in north-western China
Watersheds Ecological restoration Structural adjustments in local economy
Measures Expected policy outcomes Measures Results by 2018
Hei River •Transfer of ecological ?water through the ?Huangzangsi Water ?Control Project •Upstream: 40% ?increase in grassland ?coverage area; 20%–35% ?increase in forest ?coverage
•Midstream: reducing ?water shortage in dry ?seasons
•Downstream: Increase ?the size of East Juyan ?Lake to 35 km2 by ?2010
•Reduce water use in ?agriculture
•Introduction of water-?saving crop cultivation
•Water use in agriculture ?decreased by 1%–2%
•Ratio of water use between ?Irrigation and other use in ?agriculture decreased by ?1%–2%
Tarim River •Release 6 billion m3 ?of ecological water to ?the terminal lakes in ?18 consecutive years
•Channelization of the ?river course
•4 meter increase of ?Underground water ?table
•Protection of shelter ?belts along the river ?course
•Restoring terminal ?lakes and expansion ?of wetlands in ?downstream areas.
•Introduction of water-?saving crop ?cultivation ?Decreasing area of ?cultivated land by ?330,000 mu
•Water fee price system
•Area of cultivated land ?increased significantly ?from 2001 to 2014
Shiyang River •Protecting and ?restoring forest and ?grassland areas
•Release of 3800 m3 of ecological water
•Reduce its ?agricultural water ?usage to 170 million ?m3 a year by 2020
•Annual Inflow to ?Minqin’s Caiqi ?observation point ?increase to ?290 million m3 ?by 2020
•70 km2 wetland area ?where the groundwater ?level would be less ?than 3 m deep by 2020
•Annual groundwater ?extraction in Minqin ?reduced to 86 million ?m3 by 2020
• Restoration of forest ?and grassland coverage? in headwater region
•Expansion of ?greenhouse ?horticulture
•Reducing per capita ?cultivation areas to ?2.5 mu
•Installing scalar ?pricing system for ?groundwater and ?surface water
•Promotion of ?husbandry
•Expansion of ?large-scale farms
•Cultivation area in the ?watershed reduced by 6023 ?hectares
•Expansion of large-scale ?farms and husbandry ?operations
Shule River •Release ecological ?water to the terminal ?wetlands and ?Crescent Spring
•Expansion of ?anti-seepage canals
•Channelization of the ?Shule and Dong ?River courses
•Reemergence of ?wetlands near Hala Nor ?in Xihu National ?Reserve
•Protecting Crescent ?Spring by establishing ?Xihu National Reserve ?of Dunhuang in Gansu ?Province
•Building Water rights ?management ?institutions
•Promotion of ?greenhouse ?horticulture
•Establishing scalar ?pricing for surface ?water and ?groundwater resources
•Water use efficiency ?increased
•Irrigation engineering ?projects covered 93% of the ?cropland
•Expansion of cash crops ?cultivation
Tab.4  Ecological restoration and economic structural adjustments of the IWRM programs in north-western China
Fig.3  Institutional constraints, implementation gaps and governance uncertainties of IWRM programs in north-western China.
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