The planning, design, operation, and utilization of an integrated observational-modeling system involves many elements, or stages. Some of these are scientific or technological, whereas others are organizational or social. Eight such elements are summarized here.
These include (1) defining goals, which may include specific “deliverables” for a narrowly defined research project or flexible targets when the project is established for broader and potentially changing uses; (2) building an initial team with appropriate expertise to define and oversee accomplishment of the goals, but often allowing the team to change over time as a project evolves; (3) designing the project to achieve the goals, either specifically or with flexibility to allow for multiple-use data; (4) collecting and validating the data, integrating and validating new data collection methods as appropriate over time; (5) organizing the large data sets for a variety of different uses; (6) integrating observations across sensors and networks; (7) merging the integrated observations with models and model validation; and (8) delivering the information products from the integrated observations and merged observation-modeling to those applying them to flood and drought forecasting, water management planning, disaster response, source water protection, and other areas.
These eight elements often must be addressed in an iterative fashion as a project evolves. For example, once information is delivered, managers or other members of the scientific community may suggest changes to an ongoing project to meet additional or changing needs. The elements are discussed briefly below and are either explicitly or implicitly part of the studies summarized in Chapter 4. As the case studies were initiated for different reasons and are ongoing, each shines a light on different elements or sets of elements.
Defining project goals and “deliverables” is, of course, part of any pro-
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Appendix B
Planning, Designing, Operating, and
Utilizing the Results from an Integrated
Observational-Modeling System
The planning, design, operation, and utilization of an integrated observa-
tional-modeling system involves many elements, or stages. Some of these are
scientific or technological, whereas others are organizational or social. Eight
such elements are summarized here.
These include (1) defining goals, which may include specific “deliverables”
for a narrowly defined research project or flexible targets when the project is
established for broader and potentially changing uses; (2) building an initial
team with appropriate expertise to define and oversee accomplishment of the
goals, but often allowing the team to change over time as a project evolves; (3)
designing the project to achieve the goals, either specifically or with flexibility
to allow for multiple-use data; (4) collecting and validating the data, integrating
and validating new data collection methods as appropriate over time; (5) orga-
nizing the large data sets for a variety of different uses; (6) integrating observa-
tions across sensors and networks; (7) merging the integrated observations with
models and model validation; and (8) delivering the information products from
the integrated observations and merged observation-modeling to those applying
them to flood and drought forecasting, water management planning, disaster
response, source water protection, and other areas.
These eight elements often must be addressed in an iterative fashion as a
project evolves. For example, once information is delivered, managers or other
members of the scientific community may suggest changes to an ongoing pro-
ject to meet additional or changing needs. The elements are discussed briefly
below and are either explicitly or implicitly part of the studies summarized in
Chapter 4. As the case studies were initiated for different reasons and are ongo-
ing, each shines a light on different elements or sets of elements.
(1) Defining project goals and “deliverables” is, of course, part of any pro-
187
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188 Appendix B
posal process. In some cases, these goals appear to be deceptively straightfor-
ward. For example, for the Comprehensive Everglades Restoration Plan (see
Chapter 4), “The overarching objective of the Plan is the restoration, preserva-
tion, and protection of the South Florida ecosystem while providing for other
water-related needs of the region, including water supply and flood protection”
(Water Resources Development Act of 2000). However, enormous amounts of
time and energy have been—and continue to be—invested to define what “resto-
ration” constitutes, and what the end points might be. Major multidisciplinary
scientific initiatives wrestle with integrating multiple objectives, such as under-
standing fundamental processes such as streamflow generation, investigating
scaling relationships of observations over time and space, understanding behav-
ior under extreme conditions, and developing new instrumentation. The more
multidisciplinary the project the more difficult—and more critical—it is to es-
tablish one’s goals at the onset. In many cases, it is essential to allow the goals
to change over time as new methods are developed, new ideas evolve, and new
researchers add to both the needs and the capabilities of the project.
(2) Building a strong, interdisciplinary team, when the project spans disci-
plines, is as essential as it is supremely challenging. As one participant in an
NRC workshop expressed it, “A ‘multidisciplinary’ team is put together and
they work in isolation until the very end, when they fight.” Some of the difficul-
ties are neither scientific, nor institutional, but personal. Keys to success in put-
ting together an interdisciplinary group include finding colleagues who work at
institutions that have policies and practices that lower barriers to interdiscipli-
nary scholarship, and are willing to “immerse themselves in the languages, cul-
tures, and knowledge of their collaborators” (NRC, 2004).
(3) Designing a project to achieve the goals set out, whether narrow or
broad, specific or flexible, is the next step. An overall approach for the particu-
lar needs of interdisciplinary collaborations is described in Benda et al. (2002)
as follows:
[T]he success of interdisciplinary collaborations among sci-
entists can be increased by adopting a formal methodology
that considers the structure of knowledge in cooperating disci-
plines. For our purposes, the structure of knowledge com-
prises five categories of information: (1) disciplinary history
and attendant forms of available scientific knowledge; (2) spa-
tial and temporal scales at which that knowledge applies; (3)
precision (i.e., qualitative versus quantitative nature of under-
standing across different scales); (4) accuracy of predictions;
and (5) availability of data to construct, calibrate, and test pre-
dictive models. By definition, therefore, evaluating a structure
of knowledge reveals limitations in scientific understanding,
such as what knowledge is lacking or what temporal or spatial
scale mismatches exist among disciplines.
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Appendix B 189
This process, if followed at the project formulation stage, can be used to
construct “solvable problems”, and involves building consensus among team
members with respect to precision requirements, scales of analysis, and discipli-
nary expertise needed. A further advantage is that it leads to a feedback loop to
examine whether the project goals and “deliverables” as originally conceived
may need to be modified or rejected (Benda et al., 2002).
(4) Collecting and validating data as it relates to sensors is covered in
Chapter 2. Other aspects of data collection and validation, while central to inte-
grated observing systems, is beyond the scope of this report. This is clearly an
enormous field by itself. The Environmental Protection Agency’s Field Opera-
tions Manual for Wadeable Streams (EPA, 1998) details protocols for a wide
variety of activities from stream discharge measurements to periphyton sam-
pling. The U.S. Geological Survey lists method, sampling, and analytical proto-
cols for a variety of dissolved solutes and suspended materials at http://water.usgs.
gov/nawqa/protocols/ methodprotocols.html, and biological sampling, habitat, and
laboratory protocols at http://water.usgs.gov/nawqa/protocols/bioprotocols.html.
(5) The organization of data-sets is another important step. It is dealt with
in this report in the context of smart sensors and sensor networks, which can
help to avoid the collection of large amounts of time series data at times when
little change is occurring in the measured parameter, and to reduce data where
this is deemed useful. With satellites, the amount of data generated can be
enormous—on the order of a terabyte per day for a single satellite (NRC, 2000a)
and thus overall several thousand terabytes per year. In fact, in many cases the
size of the data archives is growing faster than we can derive information from
them; NASA’s Earth science data holdings increased by a factor of six between
1994 and 1999 and then doubled again from 1999 to 2000 (Climate Change Sci-
ence Program, 2003). However, this is also a highly parameter-specific activity,
and it is difficult to generalize principles without a specific context.
(6) Integrating observations across sensors and networks: Currently vast
amounts of environmental and water-related information are collected daily by a
wide range of sensors, and these data are being used widely for water manage-
ment, water-quality monitoring, flood hazard forecasting, and so forth. Exam-
ples of such applications are provided in the case studies in Chapter 4. Sensors
range from snow measurements taken manually by the National Weather Ser-
vice to experimental embedded network sensors to control storm water dis-
charge. And in between, there is a tremendous range of operational and experi-
mental sensor platforms or stations that collect, store, and transmit data in a va-
riety of ways. Currently, most sensor platforms are unable to communicate di-
rectly with each other, and there is a lack of inter-operability among data net-
works, for the most part, which will be discussed below.
New developments in sensor technology are occurring rapidly, both in the
ability to obtain measurements in new novel ways (for example, through biosen-
sors for water quality) and in transmitting the information through long-lived
self-configuring embedded networked sensing systems. In brief, these networks
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190 Appendix B
embed a computational intelligence in the environment, linking sensor pods
through wireless technology in a manner that allows the network to conduct
adaptive monitoring and real-time control. Development of new sensors from
nanosensors to new satellite-based systems was also described in Chapter 2.
(7) Merging observations with models: Data sets are frequently assimilated
into models, both to provide model-based forecasts (e.g., upper air observations
used for weather forecasting; precipitation and river stage observations to fore-
cast flood stages) and to predict variables not well measured (e.g., nonpoint pol-
lution runoff, terrestrial evaporation).
(8) Using results from an integrated observational-modeling system: Data
and model products have no value unless they are used. They can only be used
if they can be easily discovered, acquired, and understood in a timely manner to
those who wish to apply them to practical issues such as flood forecasting, water
availability modeling, and ecological flows, as inputs to decisionmaking. The
communication and delivery of data and information to such end users is the
back-bone to a beneficial integrated system. New “web-based hydrologic ser-
vices” are being developed at the University of Texas by Professor David
Maidment under National Science Foundation funding, and similar applications
with remote sensing at the University of Illinois by Professor Praveen Kumar
(Box 3-1). These nascent activities facilitate data discovery, acquisition, and
integration need to be further developed and integrated with users through dem-
onstration projects; and other competing approaches need to be developed and
evaluated through similar means.