The Missouri River basin extends across portions of ten states in the Midwest and Great Plains—and covers roughly one-sixth of the continental United States (Figure 1-1). Up until the mid-twentieth century, the mainstem Missouri River freely migrated back and forth across its wide floodplain. The Missouri was a shallow river and in some areas it assumed a braided pattern with no single, distinct river channel. Before construction of river engineering structures in the twentieth century, the Missouri was well known for its frequent floods, some of them severe. This “unruly river” (Schneiders, 1999) posed flood risks to cities along its course including Omaha, Kansas City, and St. Joseph, Missouri. In rural areas, the river’s flooding regime inhibited extensive agricultural use of floodplains.
There was a public desire to moderate these adverse effects of flooding, as well as meet demands for reliable water supplies for irrigation and for cities, hydropower production, and a reliable navigation channel. To satisfy these demands, a network of dams and bank stabilization projects was constructed on the Missouri River mainstem and its tributaries, much of it after World War II, with the intent of controlling and then managing the volumes and patterns of flow of both water and sediment in the river.
Congress authorized most of the mainstem dams on the Missouri River in the Flood Control Act of 1944. The dams were built following the broad outlines of the “Pick-Sloan Plan,” a merger of plans for Missouri River basin developed by the U.S. Army Corps of Engineers and the U.S. Bureau of Reclamation. The Corps of Engineers constructed mainstem dams to promote flood control, commercial navigation, and other related purposes, while the Bureau of Reclamation was given responsibility for water devel
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1
Introduction
T
he Missouri River basin extends across portions of ten states in the
Midwest and Great Plains—and covers roughly one-sixth of the
continental United States (Figure 1-1). Up until the mid-twentieth
century, the mainstem Missouri River freely migrated back and forth across
its wide floodplain. The Missouri was a shallow river and in some areas
it assumed a braided pattern with no single, distinct river channel. Before
construction of river engineering structures in the twentieth century, the
Missouri was well known for its frequent floods, some of them severe. This
“unruly river” (Schneiders, 1999) posed flood risks to cities along its course
including Omaha, Kansas City, and St. Joseph, Missouri. In rural areas, the
river’s flooding regime inhibited extensive agricultural use of floodplains.
There was a public desire to moderate these adverse effects of flood-
ing, as well as meet demands for reliable water supplies for irrigation and
for cities, hydropower production, and a reliable navigation channel. To
satisfy these demands, a network of dams and bank stabilization projects
was constructed on the Missouri River mainstem and its tributaries, much
of it after World War II, with the intent of controlling and then managing
the volumes and patterns of flow of both water and sediment in the river.
Congress authorized most of the mainstem dams on the Missouri River
in the Flood Control Act of 1944. The dams were built following the broad
outlines of the “Pick-Sloan Plan,” a merger of plans for Missouri River
basin developed by the U.S. Army Corps of Engineers and the U.S. Bureau
of Reclamation. The Corps of Engineers constructed mainstem dams to
promote flood control, commercial navigation, and other related purposes,
while the Bureau of Reclamation was given responsibility for water devel-
13
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14 MiSSOuRi RivER PlANNiNg
FIGURE 1-1 Missouri River basin, major tributary streams, and mainstem dam and
reservoirs. © International Mapping Associates.
Figure 1-1.eps
bitmap
opment along tributary streams and for irrigation. In addition, private enti-
ties and the U.S. Department of Agriculture (USDA) built dams of different
sizes on the tributaries further, affecting water flow and sediment transport.
Also, the USDA and the states encouraged private landowners to implement
practices that would hold water and sediments on their farms and ranches.
In the 1945 Rivers and Harbors Act, Congress authorized the Missouri
River Bank Stabilization and Navigation Project (BSNP). This act resulted
in channelization of most of the Missouri River below Sioux City, Iowa—a
process that had begun in the nineteenth century—via a combination of
dikes, revetments, and other engineering structures. Today, the dams and
bank stabilization projects are maintained and operated by the Corps,
Reclamation, and other entities. Management objectives of the system are
hydropower generation, recreation within the pools and in reaches be-
tween the structures, reliable municipal and irrigation water supplies, fish
and wildlife, and maintenance of a commercial navigation channel. In the
process of impounding and channelizing the Missouri River, the Pick-Sloan
dams and the BSNP projects have provided numerous economic and social
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15
iNTRODuCTiON
benefits. Implementation of these projects has also had extensive and lasting
implications for the river’s hydrologic, sedimentary, and ecological systems.
As the Missouri’s hydrologic regime became increasingly controlled, the
river basin’s sediment regime—including the processes of sediment erosion,
transport, and deposition—also was changed dramatically. Active migra-
tion of the Missouri River channel and the recycling of its floodplain largely
ceased, and the Missouri’s chutes and sloughs, islands and sandbars, oxbow
lakes, and backwater areas went from being dominant to remnant features
of the landscape. Many of the native species that had adapted to that river
and floodplain, and its aquatic and terrestrial habitats were reduced in
population, with some listed as threatened and endangered species.
In addition, the historic volumes of sediment formerly transported
downstream by the Missouri River were dramatically reduced. At the
river’s mouth near St. Louis, the preregulation Missouri River delivered
large amounts of sediment into the Mississippi River that were transported
farther downstream and that eventually contributed to deltaic sedimentary
processes in coastal Louisiana. Today that sediment supply delivered to
the mouth of the river has been reduced to one-third or less of its former
volume (Meade and Moody, 2009).
Changes to the river’s sediment regime initiated by the mainstem dams
and bank stabilization and channelization projects have had a variety of
impacts. For example, the river channel immediately downstream of both
mainstem and tributary dams has degraded and lowered because of erosive
forces of clear-water releases from the dams. Lowered riverbed elevations
downstream of the dams in heavily used recreational areas are a matter
of concern for river users. There also are threats associated with lowered
riverbed elevations, as this may undercut flood protection works, municipal
intakes, and bridges across the mainstem river and tributaries (these latter
problems are all seen in and near Kansas City, for example). Of particular
note is that three native fish and bird species on the Missouri mainstem—
the pallid sturgeon, the least tern, and the piping plover—are today listed
under the federal Endangered Species Act as threatened or endangered
(USFWS, 2000). The declines of these species have been attributed to the
river engineering projects that created a colder, deeper, and less turbid river,
and to the loss of large areas of sandbar habitat.
The Corps of Engineers has recognized and taken actions to address
the adverse consequences of river development on these three species, in
compliance with the terms of a Biological Opinion of 2000 (and amended
in 2003) issued by the U.S. Fish and Wildlife Service (FWS) under its Endan-
gered Species Act (ESA) responsibilities (USFWS, 2000, 2003). The expecta-
tions of the Biological Opinion have made sediment management a focus
of attention since 1989 when consultation began between the FWS and
the Corps. The Biologic Opinion of 2000 and the 2003 amendment identi-
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16 MiSSOuRi RivER PlANNiNg
fied alternatives and measures to prevent species extinction and included
requirements to construct shallow water habitat to improve conditions for
the pallid sturgeon and to build emergent sandbar habitat to benefit the two
listed bird species. Habitat creation targets in the 2000/03 Biological Opin-
ion were defined as acres of habitat created by these construction activities.
The Corps’ habitat construction activities, however, met with resistance—
specifically, in Missouri—where it was argued that discharging sediment
into the river as the habitat was being constructed violated federal and state
water pollution control laws (these topics are discussed in greater detail in
Chapter 3). It also was argued that adverse effects of such discharges on
water quality may be felt not only locally, but also far downstream in the
Gulf of Mexico. The Corps argued for the need to restore a portion of the
river’s sediment regimes and cited the authority of the Biological Opinion.
Meanwhile, in this historically sediment-rich river, additional sediment
might not only support the recovery of native species, but also reduce the
extent of channel bed lowering, and partially restore sediment supply de-
livered to coastal Louisiana.
Increasing attention to sediment management along the Missouri River
and the associated conflicts, demands understanding of river hydraulics
and geomorphic processes, relationships between physical responses and
habitat quality, and the relationship of sediment management to water
quality in a formerly sediment-rich river such as the Missouri. Presently,
most direct sediment management responsibilities on the Missouri River
mainstem lie with the U.S. Army Corps of Engineers, under the agency’s
flood control and navigation authorities, and its responsibilities for habitat
loss mitigation.
In 2008, to provide independent advice on Missouri River sediment and
related resource management decisions, the Corps of Engineers requested
that the National Research Council (NRC) Water Science and Technology
Board (WSTB) convene an expert committee to address seven sediment-
related questions for the Missouri River system. In response to that request,
the NRC appointed the Committee on Missouri River Recovery and Associ-
ated Sediment Management issues. (Box 1-1 contains the committee’s full
statement of task.) The breadth of the task statement required this commit-
tee to assume a broad and long-term perspective on sedimentary processes
in the Missouri River and how they have changed over time. Discussion
and explanation of the sediment regime of the Missouri River, how it has
changed over time, and its roles in many river management decisions, are
central themes of this report. Those discussions relate to several parts of
this report, including the role of sediments in Gulf of Mexico hypoxia (task
2), land building in the Gulf (task 3), Missouri River water quality (task 4),
species recovery and bed lowering (task 5), and future management actions
(tasks 6 and 7).
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iNTRODuCTiON
BOX 1-1
Committee on Missouri River Recovery and Associated
Sediment Management Issues
Statement of Task
1. How and why is sediment a significant variable in the environmental
restoration of a river system like the Missouri River?
2. What is the significance of the Missouri River sediments to the Gulf of
Mexico hypoxia problem?
3. What is the significance of the Missouri River sediments to the restora-
tion of Louisiana coastal wetlands?
4. What are the key environmental and economic considerations regarding
nutrient loads and/or contaminants in Missouri River sediment? To what extent can
such issues be addressed with management strategies?
5. Are there long-term consequences to the lack of sediment in the system
to the human environment, either environmentally or economically?
6. Are there alternatives for reintroducing sediment into the system? What
are they, and what are the key constraints surrounding these alternatives?
7. Are current Corps’ management strategies, restoration tools (e.g., chan-
nel widening, creation of chutes, shallow water habitat, etc.), and other activities
adequate and comprehensive enough to address issues associated with sediment
and nutrients in the system? If not, how might such strategies and activities be
improved?
This report provides information and recommendations of interest to
a broad audience, including several federal agencies—namely, the Corps
of Engineers, the FWS, and the U.S. Geological Survey; the U.S. Congress
and congressional staff members; Missouri River basin state governments
and citizens; nongovernmental organizations; Missouri River communities
and citizens, commercial sectors, such as navigation and recreation; and
river science and management experts from academia, the private sector,
and elsewhere.
Responses to the questions posed in this report’s statement of task
about sediment management and nutrient loadings into the river system are
not based solely in science or engineering. Rather, they also are grounded
within a larger context that includes federal and state water laws and acts,
governmental decision-making processes, and the history of settlement and
economic development along the river. Therefore, in addition to the science
of Missouri River sediment dynamics and ecology, this report discusses, for
example, authorizations for Corps of Engineers dam and bank stabiliza-
tion projects, federal laws (e.g., the Clean Water Act and ESA) that relate
to sediment management actions, and organizations with decision-making
responsibilities for sediment and related resources.
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18 MiSSOuRi RivER PlANNiNg
There is considerable overlap among the seven topic areas presented in
the statement of task to this committee. It was neither practical nor efficient
to arrange the report chapters according to that list. The resulting sequence
of chapters addresses those seven tasks, but does not correspond directly to
the questions defined in the statement of task.
Chapter 2 addresses topics of Missouri River sediment, the setting
and history of the river, and sediment-related processes. It addresses ques-
tions 1 and 5—the significance of sediment, and consequences of a lack of
sediment.
Chapter 3 discusses the governance structure—laws, authorities, and
institutions—for Missouri River management. It provides background on
organizations and river management initiatives that are referred to in sub-
sequent chapters and offers advice for improving Missouri River recovery
and management actions.
Chapter 4 discusses the consequences for ecosystems and species of
various sediment management actions. It addresses question 7—Corps of
Engineers Missouri River restoration strategies.
Chapter 5 discusses implications to the river’s sediment regimes of vari-
ous sediment management actions. It addresses questions 3 and 6—sediment
management alternatives, and constraints and prospects for improvement.
Chapter 6 discusses Missouri River water quality and sediment. It
addresses questions 2 and 4—effects of sediment management on Gulf hy-
poxia, and the challenges of designing a water quality management system
for a river like the Missouri mainstem.
Chapter 7 is a short epilogue that presents some observations regard-
ing science and decision making for Missouri River sediment and related
resources.