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496 1 MAY 2015 • VOL 348 ISSUE 6234 sciencemag.org SCIENCE
Precision medicine comes to
psychiatry p. 499
Secure sustainable seafood
from developing countries p. 504INSIGHTS
Goodbye to a large dam. Elwha River passing through the remains of Glines Canyon Dam on 21 February 2015.The
former Lake Mills can be seen in the background.
PERSPECTIVES
F
orty years ago, the demolition of
large dams was mostly fiction, nota-
bly plotted in Edward Abbey’s novel
The Monkey Wrench Gang. Its 1975
publication roughly coincided with
the end of large-dam construction in
the United States. Since then, dams have
been taken down in increasing numbers
as they have filled with sediment, become
unsafe or inefficient, or otherwise outlived
their usefulness (1) (see the figure, panel
A). Last year’s removals of the 64-m-high
Glines Canyon Dam and the 32-m-high
Elwha Dam in northwestern Washington
State were among the largest yet, releasing
over 10 million cubic meters of stored sedi-
ment. Published studies conducted in con-
junction with about 100 U.S. dam removals
and at least 26 removals outside the United
States are now providing detailed insights
into how rivers respond (2, 3).
A major finding is that rivers are resil-
ient, with many responding quickly to
dam removal. Most river channels stabilize
within months or years, not decades (4),
particularly when dams are removed rap-
idly; phased or incremental removals typi-
cally have longer response times. The rapid
physical response is driven by the strong
upstream/downstream coupling intrinsic
to river systems. Reservoir erosion com-
monly begins at knickpoints, or short steep
By J. E. O’Connor,1
J. J. Duda,2
G. E. Grant3
Dam removals are
reconnecting rivers in
the United States
ECOLOGY
PHOTO:JOHNGUSSMAN/JGUSSMAN@DCPRODUCTIONS.COM
1000 dams
down and
counting
Published by AAAS
1 MAY 2015 • VOL 348 ISSUE 6234 497SCIENCE sciencemag.org
reaches of channel, that migrate
upstream while cutting through
reservoir sediment. Substan-
tial fractions of stored reservoir
sediment—50% or more—can be
eroded within weeks or months
of breaching (4) (see the figure,
panel B). Sediment eroded from
reservoirs rapidly moves down-
stream (5, 6). Some sediment is
deposited downstream, but is of-
ten redistributed within months.
Many rivers soon trend toward
their pre-dam states (5, 7).
Migratory fish have also re-
sponded quickly to restored river
connectivity. Removal of a dam on
Virginia’s Rappahannock River in-
creased American eel populations
in Shenandoah National Park, 150
km upstream (8). Similarly, follow-
ing a small dam removal in Maine,
sea lamprey recolonized newly ac-
cessible habitat, increasing abun-
dance and nesting sites by a factor
of 4 (9). Within days of the blast
removing the last of Glines Can-
yon Dam, Elwha River Chinook
salmon swam upstream past its
rocky abutments. Responses have
been mixed for less mobile bot-
tom-dwelling plants and animals
in former reservoirs and down-
stream channels (10, 11).
Dam size, river size, reservoir
size and shape, and sediment
volume and grain size all exert
first-order controls on physical
and ecological responses to dam
removal. Larger dam removals
have had longer-lasting and more
widespread downstream effects
than the much more common small-dam
removals (4). Local environmental and habi-
tat conditions and the dam’s position in the
watershed also affect physical and ecologic
consequences. In the case of the Elwha
River, both dams were near the river mouth,
minimizing the extent of downstream ef-
fects while reconnecting large areas of high-
quality fish habitat upstream in Olympic
National Park.
Removals can also have additional con-
sequences, some of them unintended. For
example, changes to a headwater fish as-
semblage occurred when a removal allowed
upstream colonization by reservoir species
present behind a dam farther downstream
(12). Watershed contaminants, organic accu-
mulations, nutrients, once-inundated struc-
tures, and landforms from past land uses
may be uncovered and sometimes mobilized
by dam removal.
Numerical and physical models have
guided removal and monitoring strategies,
forecast broad-scale trends, and helped
avoid negative outcomes (13), but cannot
yet predict fine-scale changes driving many
ecological processes. Quantitative models of
species and ecosystem responses to dam re-
moval lag even further behind.
Most dam-removal studies so far have
been short-duration and opportunistic. Most
dam-removal analyses are from the northern
United States. Few removals have markedly
altered flow and/or released large volumes of
fine sediment. Furthermore, studies truly in-
tegrating biological and physical responses
are rare. Common protocols, more coordi-
nation among disciplines, and longer, more
systematic monitoring and research would
benefit future syntheses (13).
Coming down. (A) U.S. dam removals by decade. Data from (1). (B)
Rates of reservoir sediment erosion for 16 recent U.S. dam removals.
Condit, Marmot, Glines Canyon, and Elwha dams impounded sand-
rich sediment accumulations and were removed over short periods
ranging from hours to 3 years, leading to rapid reservoir sediment
erosion. Stronach Dam was removed in several phases over 7 years,
slowing reservoir erosion (15). Data from (4).
10.1126/science.aaa9204
1
U.S. Geological Survey, Portland, OR, USA. 2
U.S. Geological
Survey, Seattle,WA, USA. 3
USDA Forest Service, Corvallis, OR,
USA. E-mail: oconnor@usgs.gov
In the United States, many dam remov-
als have improved ecosystem function while
avoiding catastrophic consequences to either
ecosystems or human uses. The high pace
of dam removal will likely continue. But the
future is murky. As mostly small dams con-
tinue to come down, dam-removal advocates
will gaze up at the many large and ecologi-
cally disruptive dams across the country that
are decaying and filling with sediment. Deci-
sions regarding these dams will require bal-
ancing risks, continued economic function,
and the potential for ecologic restoration.
Also clouding the future is climate change,
which is likely to increase the demand for
fresh-water storage, both as a low-carbon en-
ergy source and for consumptive use.
Dams are also being removed internation-
ally; the 26 removals with published studies
are just a sample from a total probably num-
bering in the hundreds. Like most of those in
the United States, many are small structures
at the end of their useful lives. And many re-
movals, such as the ongoing one of Japan’s
Arase Dam, are motivated by economic and
ecological considerations similar to those
spurring U.S. dam removal.
The total number of U.S. and international
removals are, however, more than offset by a
renewed global boom in dam construction,
chiefly for hydropower and in regions with
emerging economies, such as Southeast Asia,
South America, and Africa (14). But the dams
of this ongoing boom will also age, just like
those of the U.S. dam-building heyday. Dam
removal looks like an activity with a long fu-
ture ahead. ■
REFERENCES AND NOTES
1. www.americanrivers.org/initiatives/dams/
dam-removals-map
2. A.G.Lejon,B.M.Renöfält,C.Nilsson,Ecol.Soc.14,4(2009).
3. J.R.Bellmoreetal.,USGSDamRemovalScienceDatabase
(2015);http://doi.org/.10.5066/F7K935KT.
4. G.E.Grant,S.L.Lewis,inEngineeringGeologyforSociety
andTerritory,vol.3,G.Lollinoetal.,Eds.(Springer,
Switzerland,2015),pp.31–35.
5. J.J.Majoretal.,GeomorphicresponseoftheSandyRiver,
Oregon,toremovalofMarmotDam:U.S.GeologicalSurvey
ProfessionalPaper1792(2012).
6. A.J.Pearson,N.P.Snyder,M.J.Collins,WaterResourc.Res.
47,W08504(2009).
7. A.E.Eastetal.,Geomorphology228,765(2015).
8. N.P.Hittetal.,Trans.Am.Fish.Soc.141,1171(2012).
9. R.Hogg,S.CoghlanJr.,J.Zydlewski,Trans.Am.Fish.Soc.
142,1381(2013).
10. D.D.Tullosetal.,PLOSONE9,e108091(2014).
11. C.H.Orretal.,RiverRes.Appl.24,804(2008).
12. M.S.Kornisetal.,Aquat.Sci.10.1007/s00027-014-0391-2
(2014).
13. P.W.Downsetal.,Int.J.RiverBasinManag.7,433(2009).
14. C.Zarfl,A.E.Lumsdon,J.Berlekamp,L.Tydecks,K.
Tockner,Aquat.Sci.77,161(2015).
15. B.A.Burroughsetal.,Geomorphology110,96(2009).
ACKNOWLEDGMENTS
ThisPerspectiveisderivedfromdiscussionsandanalysisefforts
conductedbytheworkinggrouponDamremoval:Synthesisof
ecologicalandphysicalresponsesoftheU.S.GeologicalSurvey
JohnWesleyPowellCenterforAnalysisandSynthesis.
1915–251926–351936–451946–551956–651966–751976–851986–95
1996–2005
2006–2014
Numberofdamsremoved
0
100
200
300
400
500
600
2 2 2
19 18
47
147
298
548
3
Years since dam removal
0 1 2 3 4 5 6 7 8 9 10
Reservoirsedimenterosion
(%oftotalsedimentvolume)
0
20
40
60
80
100
Stronach Dam, Pine River
Glines Canyon Dam, Elwha River
Elwha Dam, Elwha River
Marmot Dam, Sandy River
Condit Dam, White Salmon River
Dam removals in the United States
B
A
Published by AAAS

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O connor et al 2015 1000 dams down & counting

  • 1. 496 1 MAY 2015 • VOL 348 ISSUE 6234 sciencemag.org SCIENCE Precision medicine comes to psychiatry p. 499 Secure sustainable seafood from developing countries p. 504INSIGHTS Goodbye to a large dam. Elwha River passing through the remains of Glines Canyon Dam on 21 February 2015.The former Lake Mills can be seen in the background. PERSPECTIVES F orty years ago, the demolition of large dams was mostly fiction, nota- bly plotted in Edward Abbey’s novel The Monkey Wrench Gang. Its 1975 publication roughly coincided with the end of large-dam construction in the United States. Since then, dams have been taken down in increasing numbers as they have filled with sediment, become unsafe or inefficient, or otherwise outlived their usefulness (1) (see the figure, panel A). Last year’s removals of the 64-m-high Glines Canyon Dam and the 32-m-high Elwha Dam in northwestern Washington State were among the largest yet, releasing over 10 million cubic meters of stored sedi- ment. Published studies conducted in con- junction with about 100 U.S. dam removals and at least 26 removals outside the United States are now providing detailed insights into how rivers respond (2, 3). A major finding is that rivers are resil- ient, with many responding quickly to dam removal. Most river channels stabilize within months or years, not decades (4), particularly when dams are removed rap- idly; phased or incremental removals typi- cally have longer response times. The rapid physical response is driven by the strong upstream/downstream coupling intrinsic to river systems. Reservoir erosion com- monly begins at knickpoints, or short steep By J. E. O’Connor,1 J. J. Duda,2 G. E. Grant3 Dam removals are reconnecting rivers in the United States ECOLOGY PHOTO:JOHNGUSSMAN/JGUSSMAN@DCPRODUCTIONS.COM 1000 dams down and counting Published by AAAS
  • 2. 1 MAY 2015 • VOL 348 ISSUE 6234 497SCIENCE sciencemag.org reaches of channel, that migrate upstream while cutting through reservoir sediment. Substan- tial fractions of stored reservoir sediment—50% or more—can be eroded within weeks or months of breaching (4) (see the figure, panel B). Sediment eroded from reservoirs rapidly moves down- stream (5, 6). Some sediment is deposited downstream, but is of- ten redistributed within months. Many rivers soon trend toward their pre-dam states (5, 7). Migratory fish have also re- sponded quickly to restored river connectivity. Removal of a dam on Virginia’s Rappahannock River in- creased American eel populations in Shenandoah National Park, 150 km upstream (8). Similarly, follow- ing a small dam removal in Maine, sea lamprey recolonized newly ac- cessible habitat, increasing abun- dance and nesting sites by a factor of 4 (9). Within days of the blast removing the last of Glines Can- yon Dam, Elwha River Chinook salmon swam upstream past its rocky abutments. Responses have been mixed for less mobile bot- tom-dwelling plants and animals in former reservoirs and down- stream channels (10, 11). Dam size, river size, reservoir size and shape, and sediment volume and grain size all exert first-order controls on physical and ecological responses to dam removal. Larger dam removals have had longer-lasting and more widespread downstream effects than the much more common small-dam removals (4). Local environmental and habi- tat conditions and the dam’s position in the watershed also affect physical and ecologic consequences. In the case of the Elwha River, both dams were near the river mouth, minimizing the extent of downstream ef- fects while reconnecting large areas of high- quality fish habitat upstream in Olympic National Park. Removals can also have additional con- sequences, some of them unintended. For example, changes to a headwater fish as- semblage occurred when a removal allowed upstream colonization by reservoir species present behind a dam farther downstream (12). Watershed contaminants, organic accu- mulations, nutrients, once-inundated struc- tures, and landforms from past land uses may be uncovered and sometimes mobilized by dam removal. Numerical and physical models have guided removal and monitoring strategies, forecast broad-scale trends, and helped avoid negative outcomes (13), but cannot yet predict fine-scale changes driving many ecological processes. Quantitative models of species and ecosystem responses to dam re- moval lag even further behind. Most dam-removal studies so far have been short-duration and opportunistic. Most dam-removal analyses are from the northern United States. Few removals have markedly altered flow and/or released large volumes of fine sediment. Furthermore, studies truly in- tegrating biological and physical responses are rare. Common protocols, more coordi- nation among disciplines, and longer, more systematic monitoring and research would benefit future syntheses (13). Coming down. (A) U.S. dam removals by decade. Data from (1). (B) Rates of reservoir sediment erosion for 16 recent U.S. dam removals. Condit, Marmot, Glines Canyon, and Elwha dams impounded sand- rich sediment accumulations and were removed over short periods ranging from hours to 3 years, leading to rapid reservoir sediment erosion. Stronach Dam was removed in several phases over 7 years, slowing reservoir erosion (15). Data from (4). 10.1126/science.aaa9204 1 U.S. Geological Survey, Portland, OR, USA. 2 U.S. Geological Survey, Seattle,WA, USA. 3 USDA Forest Service, Corvallis, OR, USA. E-mail: oconnor@usgs.gov In the United States, many dam remov- als have improved ecosystem function while avoiding catastrophic consequences to either ecosystems or human uses. The high pace of dam removal will likely continue. But the future is murky. As mostly small dams con- tinue to come down, dam-removal advocates will gaze up at the many large and ecologi- cally disruptive dams across the country that are decaying and filling with sediment. Deci- sions regarding these dams will require bal- ancing risks, continued economic function, and the potential for ecologic restoration. Also clouding the future is climate change, which is likely to increase the demand for fresh-water storage, both as a low-carbon en- ergy source and for consumptive use. Dams are also being removed internation- ally; the 26 removals with published studies are just a sample from a total probably num- bering in the hundreds. Like most of those in the United States, many are small structures at the end of their useful lives. And many re- movals, such as the ongoing one of Japan’s Arase Dam, are motivated by economic and ecological considerations similar to those spurring U.S. dam removal. The total number of U.S. and international removals are, however, more than offset by a renewed global boom in dam construction, chiefly for hydropower and in regions with emerging economies, such as Southeast Asia, South America, and Africa (14). But the dams of this ongoing boom will also age, just like those of the U.S. dam-building heyday. Dam removal looks like an activity with a long fu- ture ahead. ■ REFERENCES AND NOTES 1. www.americanrivers.org/initiatives/dams/ dam-removals-map 2. A.G.Lejon,B.M.Renöfält,C.Nilsson,Ecol.Soc.14,4(2009). 3. J.R.Bellmoreetal.,USGSDamRemovalScienceDatabase (2015);http://doi.org/.10.5066/F7K935KT. 4. G.E.Grant,S.L.Lewis,inEngineeringGeologyforSociety andTerritory,vol.3,G.Lollinoetal.,Eds.(Springer, Switzerland,2015),pp.31–35. 5. J.J.Majoretal.,GeomorphicresponseoftheSandyRiver, Oregon,toremovalofMarmotDam:U.S.GeologicalSurvey ProfessionalPaper1792(2012). 6. A.J.Pearson,N.P.Snyder,M.J.Collins,WaterResourc.Res. 47,W08504(2009). 7. A.E.Eastetal.,Geomorphology228,765(2015). 8. N.P.Hittetal.,Trans.Am.Fish.Soc.141,1171(2012). 9. R.Hogg,S.CoghlanJr.,J.Zydlewski,Trans.Am.Fish.Soc. 142,1381(2013). 10. D.D.Tullosetal.,PLOSONE9,e108091(2014). 11. C.H.Orretal.,RiverRes.Appl.24,804(2008). 12. M.S.Kornisetal.,Aquat.Sci.10.1007/s00027-014-0391-2 (2014). 13. P.W.Downsetal.,Int.J.RiverBasinManag.7,433(2009). 14. C.Zarfl,A.E.Lumsdon,J.Berlekamp,L.Tydecks,K. Tockner,Aquat.Sci.77,161(2015). 15. B.A.Burroughsetal.,Geomorphology110,96(2009). ACKNOWLEDGMENTS ThisPerspectiveisderivedfromdiscussionsandanalysisefforts conductedbytheworkinggrouponDamremoval:Synthesisof ecologicalandphysicalresponsesoftheU.S.GeologicalSurvey JohnWesleyPowellCenterforAnalysisandSynthesis. 1915–251926–351936–451946–551956–651966–751976–851986–95 1996–2005 2006–2014 Numberofdamsremoved 0 100 200 300 400 500 600 2 2 2 19 18 47 147 298 548 3 Years since dam removal 0 1 2 3 4 5 6 7 8 9 10 Reservoirsedimenterosion (%oftotalsedimentvolume) 0 20 40 60 80 100 Stronach Dam, Pine River Glines Canyon Dam, Elwha River Elwha Dam, Elwha River Marmot Dam, Sandy River Condit Dam, White Salmon River Dam removals in the United States B A Published by AAAS