LEAFLET 20 • May 2010

Manitou Stream Photo by Paul Zedler

How Best to Manage “Urban Stream Syndrome” Improving water quality: site with Arboretum staff on 23 April 2010. Accompanying her was another noted Newer, greener approaches stream ecologist, Dr. Bobbi Peckarsky, Across the nation, 37,099 river-restoration projects cost their Emeritus Professor from Cornell U., proponents and taxpayers an average of over $1 billion per now Honorary Fellow in Zoology at year (Bernhardt et al. 2005). Most had the goal of improving UW-Madison. water quality, but only a tiny minority had any monitoring How might Manitou Stream be data to allow comparison of benefits to costs—in either dollars rehabilitated? In , or unintended impacts to the environment (ibid.). Among the Bernhardt’s data for engineered most degraded rivers and streams are those that flow through approaches to abating the urban stream urban areas. In Bernhardt’s terminology, urban streams are Dr. Emily Bernhardt solution indicate an average cost of over $1 “disconnected from their floodplains and hyperconnected to their million per project, with minimal benefit watersheds,” through drainage channels and stormwater pipes. ( services) when they fail to reconnect the stream to its The Arboretum’s Manitou Stream, near the intersection floodplain. Typical projects aim to remove obstructions to flow, of Nakoma Road and Manitou Way, fits this description. grade the banks (which releases sediment during construction), Following are answers to three questions: How would ecologists then stabilize streambeds and banks with riprap and turf restore Manitou Stream; how do engineers propose to control reinforcement matting. Environmental scientists offer newer, stormwater at Manitou Way; and what role will the public and greener and less costly approaches. regulators play in evaluating alternative approaches? Dr. Bernhardt envisioned Manitou Stream being easily and cheaply cured of its syndrome. To rebuild the streambed How would ecologists enhance and reconnect the stream to its now-elevated floodplain, she ecosystem services in Manitou Stream? proposed mimicking the activity of beavers by felling trees Like many streams that receive pulsed runoff from watersheds near the bank, creating multiple dams along the 600-ft stream covered with impervious concrete, asphalt and shingles, course, and allowing debris and sediment to accrete and raise Manitou Stream has the “urban stream syndrome” exemplified the streambed, allowing water to overflow onto its elevated by its downcut streambed and dewatered floodplain, caused by floodplain. That process had already begun behind a tree dam urbanization, which in turn alters hydrological conditions by that developed on its own during 2009. A build-up of debris and increasing flood peaks and eroding streambeds and banks. sediment had elevated the streambed. Bernhardt and Peckarsky Thanks to a grant from UW’s Women in Science and saw that the tree dam had been removed recently and predicted Engineering Leadership Institute, Dr. Emily Bernhardt that the highly-functional debris deposit and its rich microbial spoke on campus (22 April 2010) about the nation’s costly and community would be washed away by the next stormwater pulse disappointing efforts to improve water quality by removing trees (which likely happened during that evening’s rainfall). And the and grading streambanks. She offered her expertise on how best rocky riffle (potential habitat for stream invertebrates) that had to manage the Arboretum’s Manitou Stream while visiting the formed downstream in eddies around the tree dam was likely covered in the released sediment. 1 How do engineers propose to control stormwater at Manitou Way? Bernhardt’s vision for reconnecting all of Manitou Stream to its floodplain is not likely to be implemented, despite its “green” approach. Instead, the stream has been scheduled for major surgery under a new plan from Strand Engineering, called for by UW Facilities Planning and Management. Instead of elevating the streambed and reattaching the stream to a floodplain, Manitou Stream will be dammed to create a 2.43-acre retention basin. The principal reason is that the municipality responsible for runoff and low stormwater quality needs “credits” for managing stormwater and in an Intergovernmental Agreement signed in 2009, UW agreed to provide some of those credits by allowing the construction of Arb map and aerial view of Wingra Marsh large retention basins at the Arboretum. Two examples are already in place—a 6-acre basin Arboretum staff have proposed similar green approaches for in Southeast Marsh and a 7.2-acre treatment system just east of Manitou Stream (ARTF 2010), where the downcut streambed Curtis Prairie. plus the accumulation of 1 to 4 feet of sediment (from inflows The price tags for retention basins are high--in dollars, as and some deliberate filling) has dewatered the floodplain and well as in lost conservation land and unintended impacts. allowed box elder, cottonwood, and invasive exotic plants to Their potential for improving water quality is limited; they are become dominant where herbaceous plant cover (wet meadow?) designed primarily to allow suspended solids to settle out of the was once dominant (Loheide Class web archive, Pathak 2009). water column and to reduce and delay peak flood flows. The Bernhardt’s proposed repair would not return the system to 2.43-acre retention basin that is planned for Manitou Way would its historical condition—such a goal is no longer feasible in a settle out some of the phosphorus carried by the water, i.e., watershed that is “hyperconnected” by drainage ditches and some of that associated with sediment particles, not necessarily plagued with excess urban stormwater, nutrient discharges, the dissolved phosphorus or the phosphorus carried in floating and other human impacts. Her recommended course of action matter, such as leaves from street trees, which add phosphorus would, however, reverse the current trend of downcutting; to local lakes. Nor do retention ponds provide optimal it would reconnect the stream to its floodplain; and it would conditions for nitrogen removal or treatment of other dissolved restore valued ecosystem services, such as the retention of inorganic and organic contaminants. sediment and phosphorus, the conversion of nitrates to harmless Taxpayers might wish to ask why, then, are large retention nitrogen gas, and the reestablishment of wetland vegetation in basins considered “best management practices” by WDNR, place of the more drought-tolerant garlic mustard. given their high cost and limited ability to restore ecosystem services? One appeal is that modelers can simulate the deposition of total suspended solids that should settle out and

left to right across pages, 1904, 1937, and 2007 maps of Wingra Marsh, draft engineering plan superimposed on Manitou Stream.

2 Vertical streambank showing buried wetland soil. Photo: P. Zedler. Debris dam. Photo: P. Zedler. hence assign “credits” that the City can be allocated towards construction, contribute to the stormwater-treatment debt. their requirements under the new water-quality regulations. In The potential biological costs are equally alarming. Large other words, big basins make it cheap and easy to make big impoundments attract invasive species and provide stepping decisions, so long as no one considers the permanent impacts stones for invaders to reach natural lakes (Johnson et al. 2008). to Arboretum lands and the cost of perennial management of Impounded water becomes anaerobic in the shallow water unintended consequences. High price tags do not guarantee where cattails will invade. Soil phosphorus that is supposed to high functionality; in fact, Bernhardt’s search for evidence that be trapped until the basin needs to be dredged can actually be engineered streams outperform those restored using greener taken up by invasive cattails (Boers and Zedler 2008). Once approaches has yet to turn up convincing evidence that benefits the phosphorus moves into the cattail leaves, it is free to move outweigh costs. downstream as the vegetation breaks apart or forms buoyant The environmental costs of large retention basins are litter. Warm, nutrient-rich water also supports algal blooms, increasingly recognized. Building big basins requires big some of which are toxic to native wildlife (Sonzoni et al. 1988), machines that make big messes. When trees are removed and and standing water adds habitat for mosquitoes, some of which soils disturbed, sediments are mobilized and flow downstream carry West Nile Virus (Hamer et al. 2009). Impoundments during and after construction. These suspended solids go attract children and adults to explore and learn, and they unmeasured, but they create a debt that takes years to repay can be marvelous venues for education and research. But before there is a net removal of suspended solids by the big impoundments can also be attractive nuisances where children basin (EDF 2002; Bernhardt pers. comm.). The disruption of soil can encounter the hazards associated with deep mud, thin ice, structure and its microbial functions also mobilizes leachates toxic algae, and disease . that are filled with nutrients (EDF 2002; Fruebrodt 2009, Virlee 2010) and contaminants, which, although unmeasured during

Secret Pond was constructed in the mid 1980s, and it has collected sediment for ± 25 years.

3 Draft engineering plan 4/27/2010.

retention basin

Tree removal, seedings and plantings

field stone

retention basin Erosion mat

section across streambed

What role will the public and regulators The Arboretum’s Adaptive Restoration Task Force (ARTF play in evaluating alternative approaches? 2009) developed a detailed and innovative plan that calls for Manitou Stream to be connected to a restored floodplain According to federal law (Clean Water Act, Section 404), the (accomplished by removing some of the accumulated sediment), evaluation of plans to add “fill” to a water of the US begins with with sandbar willows used to stabilize the streambed and banks the following “sequencing process.” and willow trees to stabilize the floodplain. This “green plan” • A project must first try to avoid filling that results in does not require filling. significant impacts, usually determined on the basis of the The green plan, however, does not provide stormwater- area filled. treatment credits for the City. The fate of the green plan will • If the project cannot avoid filling then it must minimize likely depend on the wishes of the public. Is an environmentally- filling so that significant impacts are reduced to friendly, connected stream-floodplain system in the public’s best insignificance. interest? Or is another big basin in the public’s best interest? • Only if filling cannot be avoided or minimized can filling Under the Clean Water Act, the public is welcome to provide be permitted. Impacts then need to be compensated with a comments and to call for an open hearing to ensure that the mitigation plan. above issues are openly addressed.

References

ARTF (Adaptive Restoration Task Force). 2010. Restoration of Ecosystem Services: Johnson, P. T. J., J. D. Olden, and M. J. Vander Zanden. 2008. Dam invaders: A Plan for Manitou Stream. University of Wisconsin-Madison Arboretum. Impoundments facilitate biological invasions into freshwaters. Frontiers in Madison, Wisconsin. and the Environment 6: 357-363. Bernhardt, E. M. A. Palmer, J. D.Allan, G.Alexander, K. Barnas, S. Brooks, J. Carr, Loheide, S. 2008. Hydroecologic effects of stormwater inflow to Wingra Marsh. S. Clayton, C. Dahm, J. Follstad-Shah, D. Galat, S. Gloss, P. Goodwin, D. Civil and Environmental Engineering (CEE 619) web archive. University of Hart, B. Hassett, R. Jenkinson, S.Katz, G. M. Kondolf, P. S. Lake, R. Lave, J. Wisconsin. Madison. http://hydroecology.cee.wisc.edu/Stormwater/Introduction. L.Meyer, T.K. O’Donnell, L. Pagano, B. Powell, E. Sudduth. 2005. Synthesizing html U.S. river restoration efforts. Science 308: 636-637. Pathak, N. 2009. Assessment of the hydroecology of Wingra Marsh at the University Boers, A. M., and J. B. Zedler. 2008. Stabilized water levels and Typha invasiveness. of Wisconsin Arboretum. M.S. Thesis, University of Wisconsin. Madison. Wetlands 28: 676-685. Sonzoni, W., W. Repavich, J. Standridge, R. Wedepohl, and J. Vennie. 1988. A note EDF (Environmental Defense Fund). 2002. Amicus Brief No. 01-1243 filed to the on algal toxins in Wisconsin waters experiencing blue-green algal blooms. Lake Supreme Court the United States on the Borden Ranch Partnership, Angelo K. and Reservoir Management 4: 281-285. Psakopoulos, Petitioners, v. US Army Corps of Engineers, et al., Respondents. Virlee, C. 2010. Senior Thesis, Botany Dept., University of Wisconsin. Madison. PDF available from J. Zedler. Fruebrodt, Joe. 2009. Analysis of anaerobic topsoil in varying hydroperiods. Botany 699 Directed Study Report for J. Zedler. University of Wisconsin. Madison. This leaflet was prepared by Joy B. Zedler, Aldo Leopold Chair of Restoration Hamer, G. L., U. D. Kitron, T.L. Goldberg, J. D. Brawn, S. Loss , M. O. Ruiz, D. B. Ecology, UW-Madison, in consultation with Dr. Emily Bernhardt (Stream Hayes , and E. D. Walker. 2009. Host selection by Culex pipiens mosquitoes and Ecologist and Biogeochemist, ), and Dr. Bobbi Peckarsky West Nile Virus amplification. Tropical Medicine and Hygiene 80: 268–278. (Stream Ecologist, UW-Madison). Funding for Dr. Bernhardt’s visit came from IGA (Intergovernmental Agreement). 2009. Intergovernmental agreement to fund a joint stormwater management construction & improvement program within UW’s Women in Science and Engineering Leadership Institute. Layout by watersheds draining to the University of Wisconsin – Madison Arboretum. UW- Kandis Elliot. The historical aerial photo analysis and research by Nayan Pathak Madison Arboretum. and Dr. Stephen Loheide II is gratefully acknowledged. 4