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Editorial
May 5, 2014

Sensing and Cyberinfrastructure for Smarter Water Management: The Promise and Challenge of Ubiquity

Publication: Journal of Water Resources Planning and Management
Volume 140, Issue 7
In the face of a nonstationary and uncertain climate, smarter water management (SWM), which combines the ideas of both adaptive and integrated water management, has risen to prominence to ensure the sustainability and resilience of communities (Moss et al. 2013; Hering and Ingold 2012; Milly et al. 2008).
Adaptation in water management is necessary for two primary reasons. First, in a nonstationary climate, the likelihood of extreme events is increasing; thus, in the future, natural and built systems will be subjected to forces that have not yet been observed. Second, because of the complex interdependence of the physical and societal processes driving environmental change, forecasts of these forces will not be sufficient to continue to support static management practices. This is particularly true in large-scale water resource operations, in which extreme floods and droughts are underscoring the need to provide an improved real-time response to catastrophic events. However, while adaptive management holds great promise, it is also prone to failure if it is not continually informed by accurate, inclusive, and current information on the state of the system and by projections of future change.
Because water resource systems are an amalgam of interacting components that evolve over multiple spatiotemporal scales, an integrated management approach is necessary to maximize the benefits of management decisions across all of the affected components of a water resource system, including water sources, agriculture systems, storm/sanitary sewer systems, and ecosystems. Presently, no single data source is sufficient to satisfy the information needs required to map, monitor, model, understand, and manage the interactions between these component systems (McDonnell 2008), and the observational resolution of existing environmental sensors is too coarse to meet the demands of adaptive management (Berne et al. 2004).
Emerging sensing and cyberinfrastructure technologies can be used to meet the multiple data source and high-resolution needs of SWM. As sensors, microprocessors, and communication devices become increasingly powerful, smaller, and cheaper, it will be possible to embed these devices more deeply within urban and natural systems. However, substantial barriers—social as well as technical—currently exist to the integration of these devices and the data they collect into SWM systems of the future; indeed, such systems raise significant public policy concerns. The purpose of this article is to explore the role of sensing and cyberinfrastructure in SWM, focusing specifically on policy barriers that must be overcome to ensure the adoption of these new technologies.

The Promise of Ubiquitous Environmental Sensing

The pace of environmental data collection is increasing. As sensors become cheaper, larger numbers of land-based and remote sensors are being deployed in networks dedicated to collecting high-quality environmental data for both operational and scientific purposes—a trend accelerated by advances in sensing technology and data-intensive science (National Research Council 2012). Beyond these growing dedicated environmental measurement networks, data collected by the small, low-cost sensors that are embedded in everyday consumer products, such as mobile phones, have recently begun to be considered for environmental monitoring (National Research Council 2011). In combination, these dedicated scientific-quality sensors and embedded pervasive sensors present an opportunity for environmental sensors to exist nearly everywhere—in other words, these sensors present an opportunity for ubiquitous environmental sensing.

Big Water Data

As illustrated in Fig. 1, water data can possess three characteristic V’s that typify big data: volume, velocity, and variety (Madden 2012). Thus, the explosion of new data production expected from the adoption of ubiquitous sensing will usher in a new era of big water data that has the potential to transform the practice of water resources planning and management.
Fig. 1. The three V’s of big water data (images generated using weather radar data from National Climactic Data Center 2005 and spectral data from United States Geological Society 2012)
First, these data will enable scientific inquiry into the behaviors of very large-scale integrated water resource systems, allowing a number of existing knowledge gaps to be closed:
1.
What are the basin-scale and downstream consequences (water quality, stream flow, floods, droughts) of land management practices for urban growth (short-term) and climate change (long-term)?
2.
What is the impact of present stormwater and wastewater practices on downstream water quality at large scales (e.g., impacts of the Mississippi River Basin on the Gulf of Mexico)?
3.
How does the production of energy affect water resources (e.g., hydraulic fracturing), and vice versa (e.g., hydropower)?
Through investigating questions such as these, we will gain a better understanding of interdependencies between management decisions and water resource system responses. Presently, however, spatiotemporal variability in environmental and social processes challenges the application of current technologies to some of the world’s largest cities—a challenge that could be met by both increasing our understanding of managed complex behaviors of the water resource systems and by increasing the available real-time data describing the current state of the system.
Second, this vast amount of data will also facilitate the development of adaptive water management systems and deployment of an intelligent water resource infrastructure. Many cities (e.g., Singapore; Panama City, Florida; and Caceres, Spain) are currently operating or launching intelligent drinking water operations that use real-time sensor networks to detect pipe leaks and optimize drinking water operations. However, considerably fewer cities are implementing intelligent sewer systems such as Quebec City’s GO-RTC intelligent sewer system (Colas et al. 2005), which uses real-time environmental sensor data streams to increase efficiency and reduce the risk of sewer overflows. The relative rarity of intelligent sewer systems is due in part to the current challenges of accurately quantifying rainfall at spatiotemporal scales relevant to urban drainage. This limitation, combined with the challenge of integrating data from multiple sources, serves as a barrier for more integrated adaptive urban water management systems that holistically consider drinking water production, drinking water distribution, sewage and stormwater collection, and water treatment. Advances in ubiquitous water sensing will lower barriers to such integrated systems by providing access to real-time high-resolution data sets on which to base management decisions.

Challenges

Adoption barriers to ubiquitous water sensor networks are grounded in both technology and policy. The technological challenges resemble those of other big data applications (National Research Council 2013): (1) sensor hardware must be developed to quantify many of the most important physical parameters driving water resource models; (2) large volumes of data must be aggregated, processed, and analyzed; (3) new methods for referencing data streams from an increasing number of potentially mobile sensors over large geographical areas must be created; and (4) new approaches for integrating and fusing various data types available from heterogeneous sensors (e.g., video, audio, text, photos, etc.) must be pursued.
To overcome these challenges and meet the potential for big water data to inform SWM, higher-level data and model services are needed that integrate multiscale data from multiple sources into best estimates and uncertainty bounds of historical, current, and future (model predicted) environmental states that can be delivered instantly from the Cloud, in a format specified by data standards. Early prototypes have shown the promise of such approaches (e.g., Hill et al. 2011), but a significant effort would be needed to transform prototypes into an operational water data infrastructure that is sufficiently comprehensive to be truly useful. While these technological challenges are nontrivial, nonetheless the major challenges to SWM will be policy oriented.
First, leveraging embedded pervasive sensor data as part of a ubiquitous sensing network presents the opportunity for location data or other sensitive information about individual citizens to be collected, stored, and analyzed—an apparent loss of citizen privacy. Although technological solutions to the anonymization of confidential data are being explored (e.g., Kifer and Gherke 2006), the significance of the perception of citizen privacy was recently highlighted by the public response to the revelation that the U.S. National Security Agency has been collecting and mining data originating from mobile phones operating in the United States (“In secret” 2013). Like many types of data collected by sensors embedded in the built environment, these cell phone data have the potential to locate the behaviors of individuals in space and time. Thus, ubiquitous sensing of urban systems has the potential to be viewed as an Orwellian technology leading to decreased social freedom rather than increased security from natural disasters. Changing this perception will require not only convincing people of the benefit of ubiquitous sensing technology to water resources, but also addressing public concerns over what data are collected and how these data will be used and secured from unauthorized use.
Second, because data collected by ubiquitous environmental sensors will be used to support management of systems to protect human health and well-being, these systems will need to be robust to sensor errors (a technical challenge), but also the assignment of fault and liability needs to be clarified for autonomous systems. In water resources management, the consequence of poor decision making can be catastrophic: a region could exhaust its drinking water supply or a city could suffer a damaging flood. Adaptive water systems could be even more vulnerable to erroneous information if they depend solely on data without effective error checking. Intelligent, integrated infrastructure systems may also be more vulnerable to cascading failures compared with conventional isolated systems due to their elevated interdependencies. Thus, it is also important to explore liability structure in the context of intelligent systems, a dialogue that is already beginning as regulators draft provisions for driverless vehicles (Canadian Broadcast Corporation 2013).
Third, integration of data from a large number of producers complicates the issue of data ownership rights. Large discrepancies exist between federal and private-sector policies on data ownership and openness and this can impede essential public-private partnerships for ubiquitous sensing. Permission from data owners is often required for data sharing and data owners may expect to receive a portion of monetary or nonmonetary benefits that are derived from their data. In the case of negative benefits, data ownership is often used to apportion liability. Thus, without clear, transparent policies governing data ownership, such as those forged around health-care data (Evans 2011), the data integration upon which ubiquitous environmental sensing is based may never be realized.
As future sensing, computation, and communication hardware are adopted for broad use, the immense potential to address critical issues in water resources management should be realized and that will enable more resilient population centers. However, using these technologies to support the management of our most precious natural resource requires not only that the technology be robust, but also that we accept the level to which this technology has become embedded in our everyday lives.

References

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Go to Journal of Water Resources Planning and Management
Journal of Water Resources Planning and Management
Volume 140Issue 7July 2014

History

Received: Feb 24, 2014
Accepted: Feb 28, 2014
Published online: May 5, 2014
Published in print: Jul 1, 2014
Discussion open until: Oct 5, 2014

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David Hill, A.M.ASCE [email protected]
Assistant Professor, Dept. of Geography and Environmental Studies, Thompson Rivers Univ., Kamloops, BC, Canada V2C 2R5 (corresponding author). E-mail: [email protected]
Branko Kerkez
Assistant Professor, Dept. of Civil and Environmental Engineering, Univ. of Michigan, Ann Arbor, MI 48109.
Amin Rasekh, A.M.ASCE
Postdoctoral Research Associate, Zachry Dept. of Civil Engineering, Texas A&M Univ., College Station, TX 77843.
Avi Ostfeld, F.ASCE
Professor, Faculty of Civil and Environmental Engineering, Technion–Israel Institute of Technology, Haifa 32000, Israel.
Barbara Minsker, M.ASCE
Professor, Dept. of Civil and Environmental Engineering and National Center for Supercomputing Applications, Univ. of Illinois, Urbana, IL 61801.
M. Katherine Banks, F.ASCE
Professor, Zachry Dept. of Civil Engineering, Texas A&M Univ., College Station, TX 77843.

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