moriver historic vegetation change moriverclasses 10-13-11
TRANSCRIPT
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Historic landscape and vegetation
changes along the Missouri
Mark Dixon
Introduction to River Studies
October 13, 2011
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Human Alteration of Riparian Ecosystems
Flow regulation (dams)
~45,000 large (>15 m high) large dams, 800,000 small damsworldwide
Upstream effects inundation, raising water tables
Downstream effectsflow patterns, incision, reduced meanderingreduced sediment
Levees, bank stabilization, channelization
Flow diversion, river dewatering
Groundwater depletion
Land use (e.g., grazing, development)
Other disturbances (e.g., fire)
Non-native species
Climate change
Pollution
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Impounded
Remnant
Channelized
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Impacts of Missouri River
Management on Cottonwood ForestsI. Historic land use/cover change
II. Impacts on flow and sediment regimes
and cottonwood regeneration
III. Changes in species composition in
cottonwood forests
IV. Effects of changes on wildlife (songbirds)
V. Effects of flood of 2011?
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I. Historic Changes in Land Use
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Historic
Changes in
Segment 10
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Time
FlowV
olume
From: Poff et al. 1997
II. Changes in Flow & Sediment Regimes:Dams alter downstream flow patterns and flow-
dependent ecological processes
Flow attenuation
&
stabilization
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-3.5
-3
-2.5
-2
-1.5
-1
-0.5
0
0.5
1
740760780800820
WaterSurfaceE
levationC
hange
(m)
Re
lativet
o1960
River Mile (1960)
1965
1986
1994/95
2002
Channel Bed Degradation, Gavins Point Reach
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0
50,000
100,000
150,000
200,000
250,000
300,000
350,000
400,000
450,000
500,000
1930
1933
1937
1940
1943
1946
1949
1953
1956
1959
1962
1965
1969
1972
1975
1978
1981
1985
1988
1991
1994
Water
FlowatYankton(c
ubicfeetpersecon
d)
Date
The Heart Beat of a RiverLostMissouri River Flow at Yankton, SD
1930 - 1995
Ft. Peck 1937 Ft. Randall 1952Garrison 1953Gavins 1955
Oahe 1962Big Bend 1964
Mainstem Dams and Year of Closure
Slide courtesy of Wayne Nelson-Stastny, USFWS
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25 - 10 %
75 - 25 %
90 - 75 %
ROR Natural
Hydrograph
25 - 10 %
75 - 25 %
90 - 75 %
Current Water-Control
Plan
0
10
NovSepJulyMayMarJan
20
30
40
50
60
70
80
Discharge
,kcfs
Hydrologic Alteration, Sioux City, Iowa
km 1,178
Slide courtesy of Wayne Nelson-Stastny, USFWS
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Recruitment Box Conceptmodified from Mahoney and Rood (1998)
RecruitmentBand forSpecies A
DispersalInterval forSpecies A
Day of the Growing Season # of Sandbar Plots
RiverLevel
SandbarTopography
DispersalIntervals forother species
Stage decline
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(adapted from Johnson 1992)
Mathematical Model of Succession inMissouri River floodplain forests
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Projections of Cottonwood Succession Model forGarrison Reach, ND (Johnson 1992)
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Cottonwood Forest Age Map
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>114 yrs
50-114 yrs
25-50 yrs
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III. Changes inSpecies
Composition Non-native & invasive
tree species arecommon (seg. 8 & 10) White mulberry Russian olive Eastern red cedar
Native late successionalspecies are scarce onpost-dam sites
0
10
20
30
40
5060
70
80
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Historic Change in Tree SpeciesComposition on Segment 10 (59-mile MNRR)
1857-1869
(GLO Survey)
2007(field sampling)
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IV. Possible Implications of Missouri River
Changes for Forest Songbirds
Species preferring earlysuccessional (shrub/sapling)
habitats
Bells Vireo, Orchard Oriole, Yellow
Warbler Post-dam non-cottonwood (e.g.,
Russian-olive)also provides suitable
habitat
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Possible Implications of Missouri River
Changes for Forest Songbirds
Mature/old forest species Ovenbird, Eastern-Wood Pewee,
Red-eyed Vireo, Wood Thrush
Lower abundance for several in
non-cottonwood
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Possible Implications of Missouri River
Changes for Forest Songbirds
Woodpeckers, other cavity nesters Need mature and old forests (>50 years)
other cavity nesters less so
Lower abundance in non-cottonwood
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Changes Affecting Floodplain Forestson Missouri River
Loss of forest to land conversions Reservoir inundation and rising water tables upstream Increased cropland Clearing of forest
Reduced cottonwood regeneration Increasing proportion of older forests
Changes in species composition Successional change:
Decreases in cottonwood, increases in later successional trees
Terrestrialization increases in upland species
Increase in introduced and invasive species
Floodplain disconnected from river processes Channel down-cutting, flood control, levees, declining water tables
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Restoring the Missouri
Degradation of the Missouri River ecosystem will
continue unless some portion of the hydrologicand geomorphic processes that sustained the
pre-regulation Missouri River and floodplainecosystem are restored including flow pulsesthat emulate the natural hydrograph
National Research Council (2002) The Missouri River
Ecosystem: Exploring the Prospects for Recovery
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Restoring the Missouri
Native biota are keyed in to natural flowtiming and periodic floods
Fish spawning
Sandbars for plover and tern nesting Productivity of aquatic insects
Cottonwood reproduction
Replenishment of cottonwood forests foreagle nesting
Floodplain-river connections
Photo by Tim Cowman
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Ecological Functions and Flow-RegimeNaturalization
SPRING PULSE(S): BUILD BARS CONNECT FLOOD PLAIN SPAWNING CUE
SUMMER LOW: EXPOSE BARS PROVIDE SWH
NESTING TERNS AND PLOVERS
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Challenges in Missouri RiverFlow Restoration
Large, multi-purpose river, subject to socio-economic, legal and political constraints Stakeholders navigation, hydropower, land use, etc.
Endangered Species Act, Biological Opinion
Restoring or mimicking natural flows may not
restore other critical processes (e.g., sediment)
Uncertainty of ecological linkages to flowcomponents (vs. certainty of socioeconomic costs) E.g., pallid sturgeon
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Effects of Flood of 2011?
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Effects of Flood of 2011? Erosion of banks
Loss of forest?
Deposition in new areas May increase sandbar habitat
But, may also be more channel down-cutting
Prolonged inundation May cause mortality of trees
Redcedar, Cottonwood?
Effects on delta?
Policies, Other? More land set aside for conservation? New policies?
Backlash against environmental management?
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Platte River in Nebraska
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Morphology, Landforms of aBraided River
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1938 1998
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Historic Channel Changes on the PlatteRiver near Shelton, Nebraska
1938
2001
Channel Change 1938-2001
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Platte River
NEED NEW SLIDES PHRAGMITES
ALSO NEED SOME SUMMARY TEXTSLIDES FOR BOTH??? AT LEAST GIVE STUDENTS AN OUTLINE
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Platte River
NEED NEW SLIDES PHRAGMITES
ALSO NEED SOME SUMMARY TEXTSLIDES FOR BOTH??? AT LEAST GIVE STUDENTS AN OUTLINE
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Platte River
NEED NEW SLIDES PHRAGMITES
ALSO NEED SOME SUMMARY TEXTSLIDES FOR BOTH??? AT LEAST GIVE STUDENTS AN OUTLINE
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Least Tern
Sandhill Crane
Whooping CranePiping PloverPhoto by Chris Gondahl Photo by Rocky Hoffman
Photo by Jim Rathbert
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Vegetation Clearing on the Platte
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Platte River Riparian vegetation has increased with flow
regulation (dams, flow diversion) Flood not large enough to scour vegetation out of active
channel bed
Increase in low flows from irrigation returns, may increase
seedling survival during droughts
Cottonwood regeneration and area have increased! (oppositeof Missouri)
Channel has narrowed considerably since 1930s (sometimes>70%)
River morphology has become less braided, more meandering
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Platte River
Recent increases in exotic grass (Phragmites) Concerns about geomorphic effects, sandbar stabilization
Good at binding sediments and resisting floods
Could lead to further channel narrowing and loss of
sandbar habitat
Management to restore braided channel byclearing vegetation, prescribing floods, & adding
sediment Trying to restore open sandbar habitat for Whooping andSandhill cranes, Piping Plover, Least Tern
Di er ent Responses of Misso ri and
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Divergent Responses of Missouri and
Platte to Flow Regulation
Meandering rivers (Missouri) Flow regulation reduces channel meandering, creation of point bars
Recruitment of cottonwoods decreases
Long-term decline in cottonwood projected, increase in latersuccessional species
Braided rivers (Platte) Flow regulation may enhance low flows (help persistence) and reduce
high flows (reduce scour)
Facilitates colonization of the active channel bed by vegetation
Channel narrows and may shift morphology
River morphology influences response to flow regulation
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NarrowedMigration ReducedIntermediate Case
Glacial DepositLocally Derived DepositAncient Fluvial Deposit
Aeolian Deposits:
LoessSand
Friedman et al. 1998,
Wetlands, 18, 619-633
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