Dam construction in lakes may have significant negative effects on aquatic ecosystems, and it is therefore considered as a major threat to aquatic biodiversity. Many studies have been conducted to investigate how fish are affected by dam removal. Dams can impact the flora and fauna of lakes by influencing the structure of food webs and nutrient dynamics. In this study, I investigated whether or not dam removal in lake outlets affect the proportion of piscivorous perch, including a separate analysis of perch with lengths between 120-180 mm (the length interval at which the diet changes from insects to fish). I used data from 27 lakes located in Värmland, Dalarna and Västmanland. The proportion of piscivorous perch was 43% higher where the dam had been removed. The results showed a (non-statistically significant) trend on the effect of dam removal on the mean proportion of piscivorous perch. Dam removal had no effect on the mean proportion in the length interval 120>180 mm. Dams alter the composition, structure, and function of the surrounding environment; therefore, the outcomes of dam removals can be unpredictable. There are few published studies on how lentic fish communities respond to dam removals in lake outlets; therefore, such knowledge would be valuable and can provide relevant information to water managers, hydropower companies and decision-makers. / Dammkonstruktion i sjöar har betydande negativa effekter på akvatiska ekosystem, och anses därför som ett stort hot mot akvatisk biodiversitet. Det har gjorts många studier på hur fisk påverkas av dammar, och utrivning av dessa, eftersom de kan ha effekter på sjöars flora och fauna, genom att påverka näringsvävens struktur och näringsämnesdynamik. I denna studie undersökte jag om dammutrivningar i sjöutlopp påverkar proportionen av fiskätande abborrar, samt om medel-proportionen av fiskätande abborrar mellan 120–180 mm påverkas av utrivning (det längdintervall när dieten ändras från insekter till fisk). Jag använde data från 27 sjöar som var lokaliserade i Värmland, Dalarna och Västmanland. Resultaten visade att proportionen av fiskätande abborrar var 43% större där dammen hade rivits ut. Dammutrivning visade en (icke statistisk signifikant) trend på att det fanns en effekt av dammutrivning på medelproportionen av fiskätande abborrar. Dammutrivning hade ingen signifikant effekt alls på medelproportionen av fiskätande abborre i längdintervallet 120>180 mm. Dammar förändrar sammansättningen, strukturen och funktionen i den omgivande miljön, därför kan dammutrivningars resultat vara oförutsägbart. Det finns få publicerade studier av hur fiskesamhällen reagerar på dammutrivningar i sjöutlopp, därför skulle sådan kunskap vara värdefullt och kan ge relevant information till förvaltare av vatten, såsom myndigheter, kraftbolag och beslutsfattare.

Dammar har använts till många saker genom århundrandena, bland annat energiutvinning, reglering av vattennivå och transport av timmer. När dammar inte längre är i bruk och inte är ekonomiskt gynnsamma är dammutrivning en vanlig restaureringsmetod för att återställa ekosystemen. Dammar påverkar generellt ekosystemen negativt då det blir en begränsad konnektivitet inom och mellan vattendragen och sjöarna. Fiskars migration av och spridning av fröer från växter hindras av dammarna. Genom att riva ut dammar öppnas vägar för organismer att förflytta sig. Med utrivning av dammarna sker även en vattennivåsänkning som leder till att undervattensväxter kan bli mer utsatta. Undervattensväxter (makrofyter) som lever i det grunda vattnet bidrar med skydd och habitat för både fisk och bentisk fauna, samt zooplankton. Syftet med min undersökning är att undersöka om täckningsgraden av makrofyter förändras av dammutrivning. Även koncentrationen av fosfor i vattnet samt ljustillgången (mätt som siktdjup) förväntades ha en påverkan på täckningsgraden av makrofyter i sjöarna. Resultaten visade att det inte fanns ett signifikant samband mellan täckningsgraden och dammutrivning. Ett samband mellan täckningsgrad och siktdjup kunde inte heller bevisas. Däremot fanns ett positivt samband mellan täckningsgrad och koncentration fosfor i vattnet. Den här studien visar att makrofyter inte påverkas negativt av dammutrivning vilket är positivt då makrofyter har en viktig roll i ekosystemen. / Dams have been used for many things throughout history, such as an energy source, for regulation of water levels and timber transport. When dams are no longer economically viable, dam removal is a common method of restoring the ecosystem. Dams generally effect the ecosystems negatively, as they limit the connectivity in and between rivers, streams, and lakes. For example, fish migration and the spread of seeds are typically disrupted by the dams. When dams are removed, the water levels are normally reduced, which can lead to aquatic plants becoming more vulnerable. Aquatic plants (macrophytes) that grow in shallow parts of a lake provide habitat for fish, bentic invertebrate fauna and zooplankton and they thus form an important part of the limnic ecosystems. The purpose of my study was to investigate if the coverage of macrophytes changes after dam removal in lakes. Also, the concentration of phosphorus in the water and the light availability (measured with Secchi depth) were predicted to influence the coverage of macrophytes. The results showed that there was not a significant effect of dam removal or Secchi depth on the coverage of macrophytes. The concentration of phosphors had a positive significant effect of on macrophyte coverage. My study indicates that dam removal does not affect macrophytes negatively, which may be important due to macrophytes’ important role in the ecosystem.

Master of Arts / Department of Geography / Lisa M.B. Harrington / While environmental concerns have played a secondary role in dam removal rationales thus far, the Condit and Elwha removal projects could signal a change in governmental and public priorities in dam management in the United States (Born et al. 1998; Bednarek 2002). For this research, I compared two dam removal projects designed to restore native salmon runs in two rivers in Washington State: the Condit Dam on the White Salmon River and the Elwha and Glines Canyon Dams on the Elwha River. This thesis asks: given choices of preserving dams that produce clean electricity and the well-established lake-based habitats created by their reservoirs or re-establishing a free-flowing river to reestablish fish and wildlife populations, how are decisions made, and what does the process and outcome mean to local communities? Research interview data was used in combination with policy documents to answer three research questions: 1) What factors affect decision-makers’ and other stakeholders’ support for (or rejection of) dam removal? 2) How did stakeholders’ perceptions and opinions play a role in the decision-making process? and 3) What can we learn from problems and successes evident from the dam removal decision processes? The main factors influencing both the Condit Project and the Elwha Project were environmental (salmon restoration), political (meeting legislative requirements for fish passage), and economic (finding the least cost fish passage alternative). The primary motivation for both projects was salmon restoration via the provision of federally mandated fish passage. The possibility of regaining a valuable resource spurred Tribal, federal, and state agencies to advocate for the removal alternative. Dam owners in both cases desired the least cost option, resulting either in their consent to removal (Condit Project) or selling the dams and relinquishing responsibility to the federal government (Elwha Project). Both took over two decades to complete and were removed in 2011. Perceptions of the relative importance of removal/retention options and dissatisfaction with the decision-making process led to polarization of the communities affected by the dam removals and contributed to the 20+ year project timelines. In order to promote good will and understanding between decision makers and stakeholders, two lessons can be learned from the Condit and Elwha Projects: 1) actively seek to include both proponents and opponents in decision-making and 2) establish robust communication among stakeholders and decision makers. Additionally, preliminary evidence indicates that dam removal does result in movement of salmonids to river reaches that had been blocked by dams, and dam removal may also lead to unintended consequences related to local environmental quality and resource access, such as short term air quality concerns and longer term effects on groundwater availability.

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This thesis explores the background of the Klamath Basin Restoration Agreement, a 250 page water use agreement among irrigators, Indian tribes, fishermen, environmental groups, federal and state agencies in the Klamath Basin. The agreement is contextualized in terms of water rights law, Indian law and the Endangered Species Act. The specific details of the agreement are explored. Finally, this thesis evaluates the agreement's merits and suggests a path forward for the agreement to become law.

Graduation date: 2006 / Dam removal is increasingly viewed as a river restoration tool because dams affect so many aspects of river hydrology, geomorphology, and ecology; but removal also has impacts. When a dam is removed, sediment accumulated over a dam’s lifetime may be transported downstream; and the timing, fate and consequences of this sediment remain some of the greatest unknowns associated with dam removal. In this thesis, I develop a conceptual model for erosion and deposition following removal of sediment-filled dams in mountain streams, and use field studies to document actual change. The data show that reservoir erosion in mountain rivers is likely to occur by knickpoint migration, with 85% of stored sediment being released during a single storm event in two field studies, at shear stresses less than that required for mobilization of the median surface particle size. Coarse sediment is predicted to deposit close to the dam with channel aggradation decreasing exponentially with increasing distance downstream, although some channel features are shown to have a greater propensity for aggradation than others. Field studies show that turbidity associated with dam removal and reservoir erosion may decrease hyporheic exchange, but gravel deposition (e.g., 470 m3 of gravel from Dinner Creek Dam) has the potential to more than offset that decrease, and increased hyporheic exchange is shown to reduce diurnal temperature change. Macroinvertebrate density and taxa richness did not respond to dam removal itself, but rather with time-lagged reservoir erosion. Following reservoir erosion, macroinvertebrate density recovered quickly, although longterm taxa community composition appears to be altered. On the Sandy River, field measurements of shear stress and patterns of sediment deposition following cold lahars were used as an analog to predict the fate of fine sediment, which is likely to deposit far from the dam. Results show that the Sandy River has little capacity for fine sediment storage in pools above RK 6.4 (~ 42 kilometers below Marmot Dam) at discharges associated with reservoir sediment releases. Taken as a whole, this paper illustrates a complex suite of process that may accompany removal of sediment-filled dams in mountain rivers.

As ecological restoration expands as a practice, so does the complexity, cost, and scale of many projects. Higgs (2003) terms these projects technological and argues they limit meaningful community focal restoration practices, one component of good ecological restoration. The planned removals of two large dams on the Elwha River in Washington State provide a case study to investigate this theory. I conducted 18 in-depth interviews with community leaders and restoration practitioners in order to explore the question, “How do technological restoration projects enable or constrain community engagement, and in the case of the Elwha River, how might such engagement be enlarged?” This interpretive study suggests that technological restoration projects, particularly when managed by federal agencies, expand engagement through a broadened 1) public audience and 2) suite of engagement activities. I argue for a “focusing” of engagement activities, and propose a matrix for assessing opportunities for local community engagement.

Damming disrupts natural sediment flow to downstream resulting in legacy sediment accumulation. Legacy sediments have been well investigated in streams throughout the Piedmont region; however, there is no research of legacy sediments following dam removal in low-gradient Coastal Plain streams. Research objectives were to: characterize legacy sediments in a low-gradient stream restoration, quantify pre-impoundment accretion and carbon dynamics, and assess current sediment deposition rates via 14C analyses within sediment cores and sediment collection tiles. Carbon accumulation and accretion rates of modern tidal sediment have reached that of the tidal relic benchmark and current sediment deposition rates are similar between the natural reference and restored tidal wetlands. At this site, the pattern of legacy sediment accumulation and stream incision was reversed relative to previous studies in higher gradient systems. Results suggest in dam impacted Coastal Plain streams, legacy sediment may become a benefit rather than a liability for downstream tidal wetlands.