The
precautionary principle warns us not to make irreversible decisions. Yet
building a dam proves to be an irreversible decision. Someone else must deal with
dam removal much later. While dams provide services to
our communities and economies, the average age of the 90,580 dams in the USA is
56 years. Many billions of dollars are
needed to repair aging and often high-hazard structures (Source).
When
I first began studying rivers in the 1970s, the idea of removing dams for
purposes aside from safety would be heresy. Yet, more than 1,200 dams have been removed, especially in the
Northeast, Midwest, and Pacific Northwest USA (Bellmore et al. 2017). More than
half of these were demolished in the past decade! Understanding the effects of dam removal is
limited due to the rarity of before-and-after studies of biophysical
responses. Therefore, the responses to
dam removal cannot be easily generalized. Surprisingly, in a few cases, a new river channel stabilizes relatively
quickly and may even approach pre-dam morphology (see e.g., East et al. 2015). If you wish to examine dam removals in your
region, review the American Rivers dam removal database.
Dam
removal science relies on the study of basic river geomorphology and ecology. However, fewer than 10% of dam removals have
been scientifically evaluated (Bellmore et al. 2017; Foley et al. 2017) and few
studies examine important linkages between the physical and ecological
consequences. Gordon Grant, Research Hydrologist with the US Forest Service,
says “You can take a dam out all at once, or you can take it out slowly, and
the consequences for the way sediment is released are profoundly different
depending on how you do it.” (Oliver and
Grant 2017). Major uncertainties exist
as to the (1) degree and rate of reservoir sediment
erosion, (2) excessive channel incision upstream of reservoirs, (3) downstream
sediment aggradation, (4) elevated downstream turbidity, (5) drawdown impacts
on local water infrastructure, (6) colonization of reservoir sediments by
nonnative plants, and (7) expansion of invasive fish. These uncertainties hinder
the full application of dam removal as a stream restoration strategy (Tullos et
al. 2016). Removals of the 64-m-high Glines Canyon Dam and the 32-m-high Elwha Dam were well-studied. Here,
investigators revealed that mainstem riffles were restored to cobble dominance
after sediment was released and transported through the system (Peters et al.
2017).
What’s
happening in our local region? Unions and Simpkins Dam on the Patapsco River were
removed in 2010 and removal of Bloede Dam, which is a complete barrier to
upstream fish migration, is now underway (Harbold et al. 2015; Maryland DNR
2017). These dam removals will provide an
additional 65 miles of spawning habitat for blueback herring, alewife, American
shad, hickory shad, and more than 183 miles for American eel in the Patapsco
River watershed.
In Virginia, three dams were recently demolished
after decades of planning and permitting.
Harvell
dam was removed in 2014 from the Appomattox River, Virginia, permitting many
migratory American Eel, American Shad, Alewife, Blueback Herring, and Hickory
Shad to access spawning habitats over 100 miles upstream of the historic dam. Watch
the dam removal video.
Monumental
Mills Dam, built in 1816 on the Hazel River, was the 17th dam removed in the
Chesapeake Bay watershed of Virginia since 2004. It is the most recent dam removal by the Department of Game and Inland Fisheries.
The
Pigg River power dam removal was in the works for 13 years before its removal in 2016. This dam removal is outside the
Chesapeake Bay watershed and benefits the Endangered Roanoke Logperch Percina
rex as well as local paddlers.
The Roanoke Logperch exists in five isolated tributaries and the Pigg River population may now be able to expand with the removal of the dam. The Roanoke Logperch does not occupy the slow, silty habitats that existed upstream from the dam. These fish feed on benthic insects that exist in clean, well-scoured habitats. To find their prey, they often use their pointed snout to dislodge and turn over pebbles, thereby exposing their prey. To witness this unique feeding behavior, watch this underwater video taken by Derek Wheaton.
Roanoke Logperch. Photo by Chris Crippen. |
Pigg River Power Dam before (photo by USFWS) and during demolition (photo by Roanoke Times) |
Jordan’s
Point Dam, an historic cotton mill dam on the Maury River near Lexington,
Virginia, may be next on the removal list. Jordan’s Point Dam poses a drowning hazard and is a barrier for fish passage. Jordan’s Point Dam
is owned by the City of Lexington ,which is liable for lawsuits and must pay for
repairs. Maintenance and repair costs are more expensive than dam removal. In June, 2017, City Council voted to remove the dam.
Because dams change the landscape and waterscape in ways that may attract development, the
removal of dams is often met with significant opposition. This week the Millburnie Dam on the Neuse River, North Carolina, was removed. Not
all were in full agreement with the dam’s removal. Dams create novel landscapes and waterscapes
that in some cases is preferred by those growing up with the dam. One planned Massachusett dam removal was
halted as opposition grew. One protester
reflected that “You kill the dam, you are killing a part of me"
(Fox et al. 2016).
Migratory fish benefit from dam removals. The
American Shad and Blueback Herring now use over 28 additional miles of the
Rappahannock River after the Embrey Dam was removed in 2004. Furthermore, Hickory Shad, Alewife, and Striped Bass have
been documented above the Embrey Dam site, and American Eel
increased in the upper watershed. Bosher Dam on the James River, built in 1840, may
still be a bottleneck for American Shad passage even though a fish passage was constructed.
Dams removed from 1999 through 2016. Source: Caffin and Gosnell (2017). |
Dam removal trends are likely to continue as dams
age and no longer serve original purposes.
Experience indicates that permitting requires work by numerous partners
over a decade-long timeframe. The majority of US dam removals were privately
owned, non-hydropower dams, which includes many investor-owned dams. Many of
these were small and removal had minimal impacts, thereby allowing easier
permitting under federal laws. Other
dams were authorized by legislative or executive actions, will prove more
difficult to remove and removal will be subject to NEPA, ESA, and state water
quality certification under the CWA.
FERC relicensing is an opportunity to analyze choices as the FPA (Energy Policy Act of 2005, Public Law 109-58 § 241) recognizes that dams have a finite, useful lifespan and should be operated under the public interest (Chaffin and Gosnell 2017). Hydroelectric project owners should request an alternative licensing process (ALP) when substantial opposition to dam relicensing indicates a lengthy, mediated conflict resolution that may lead to decommissioning. As public opposition to existing dams builds, it is important that we systematically study the effects of dam removal. Each dam removal is a different large-scale experiment. We need to learn from each one in order to fill the gaps in our science (see below). Restoring free-flowing rivers provides many new opportunities for connecting our youth with freshwater habitats.
FERC relicensing is an opportunity to analyze choices as the FPA (Energy Policy Act of 2005, Public Law 109-58 § 241) recognizes that dams have a finite, useful lifespan and should be operated under the public interest (Chaffin and Gosnell 2017). Hydroelectric project owners should request an alternative licensing process (ALP) when substantial opposition to dam relicensing indicates a lengthy, mediated conflict resolution that may lead to decommissioning. As public opposition to existing dams builds, it is important that we systematically study the effects of dam removal. Each dam removal is a different large-scale experiment. We need to learn from each one in order to fill the gaps in our science (see below). Restoring free-flowing rivers provides many new opportunities for connecting our youth with freshwater habitats.
Gaps in the
Science of Dam Removal (Bellmore et al. 2017)
·
Only 9% of dam removals have been described in
published scientific literature.
·
No dam removal studies exist in the central
U.S., and many states have few studies relative to the number of removed dams.
·
There are few studies of the smallest dam
removals (those less than 2 m in height) relative to the prevalence of their
removal.
·
Monitoring is generally short-term (1–2 years)
and often includes little or no data prior to dam removal.
·
Fewer studies report biological and
water-quality responses to dam removal relative to physical responses (e.g.,
sediment and flow).
·
Few holistic ecosystem-level studies exist that
attempt to measure linkages among physical, water-quality, and biological
responses.
Kids snorkeling in a river. Photo: Jason Meador, Citizen Science Program Manager for Mainstream Conservation Trust. |
References
Bellmore, J.R., J.J. Duda, L.S.
Craig, S.L. Green, C.E. Torgersen, M.J. Collins, and K. Vittum. 2017. Status
and trends of dam removal in the United States. Wiley Interdisciplinary Reviews: Water 4:e1164. doi: 10.1002/wat2.1164
Chaffin, B.C., and H. Gosnell. 2017. Beyond mandatory fishways: Federal
hydropower relicensing as a window of opportunity for dam removal and adaptive
governance of riverine landscapes in the United States. Water
Alternatives 10:819-839.
East AE, Pess GR, Bountry JA, Magirl
CS, Ritchie AC, Logan JB, et al. 2015. Large-scale dam removal on the Elwha
River, Washington, USA: River channel and floodplain geomorphic change. Geomorphology 228:765–86.
https://doi.org/10.1016/j.geomorph.2014.08.028
Foley, M.M. and ten coauthors. 2017. Landscape context and
the biophysical response of rivers to dam removal in the United States. PLOS
ONE https://doi.org/10.1371/journal.pone.0180107
Fox, C.A., F.J. Magilligan, and C.S. Sneddon. 2016. “You kill
the dam, you are killing a part of me”: Dam removal and the environmental
politics of river restoration. Geoforum 70:93-104.
Harbold, W., J. Kilian, and P. Graves. 2015.
Patpsco River dam removal study: Assessing changes in American Eel distribution and aquatic communities, 2013-2014. Maryland Department of Natural Resources,
Annapolis.
Magilligan
F, Graber B, Nislow K, Chipman J, Sneddon C, Fox C. River restoration by dam
removal: Enhancing connectivity at watershed scales. Elementa 2016:4.
Oliver, M., and G. Grant. 2017.
Liberated rivers: lessons from 40 years of dam removal. Science Findings 193.
Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest
Research Station. 5 p.
Peters, R.J., M. Liermann, M.L. McHenry, P. Bakke, and G.R.
Pess. 2017. Changes in streambed
composition in salmonid spawning habitat of the Elwha River during dam removal.
Journal of the American Water Resources Association
53:871-885. DOI: 10.1111/1752-1688.12536
Tullos, D.D., M.J. Collins, J.R.
Bellmore, J.A. Bountry, P.J. Connolly, P.B. Shafroth, and A.C. Wilcox. 2016. Synthesis
of common management concerns associated with dam removal. Journal of the American Water Resources Association 52:1179-1206. DOI:
10.1111/1752-1688.12450