210 • Z.RUBIN ETAL.
<br /> Process-based restoration relies upon understanding what et al., 1993). By acknowledging a range of historic forms and
<br /> the natural forms and functions of a watershed were and can processes,we gain insight into the potential for passive resto-
<br /> be, given imposed climatological, ecological, geological, and ration,and when active restoration can be applied effectively.
<br /> land-use constraints. Failure to appropriately assess HRV of a This research investigated the HRVof a subalpine valley by
<br /> system, or to appropriately define contemporary physical analyzing stratigraphic records to quantify aggradation rates
<br /> dynamics,has resulted in several well documented restoration and processes of sediment delivery before and after European
<br /> failures such as Uvas Creek in California, USA,where restora- settlement of the region in the mid-19th century.To investigate
<br /> tion activities attempted to impose a meandering planform in HRVover a time scale of 102 to 103 years,we conducted anal-
<br /> a location where watershed history suggested a system that ysis of aerial photography, ground penetrating radar surveys,
<br /> was historically braided in response to disturbance (Kondolf, radiocarbon dating, and sediment descriptions via trenching
<br /> 2006).Innumerable other restoration projects have not achieved and coring.In May 2003,a breach in the Grand Ditch initiated
<br /> any broad ecological benefit because restoration attempted to a debris flow in Rocky Mountain'National Park that transported
<br /> impose forms that were inappropriate or unsustainable given --36,000 M3 of sediment into the Upper Colorado River and
<br /> present climate, land-use, and watershed conditions (Wohl deposited up to 1 m of sediment in the Lulu City wetland.
<br /> et al., 2005). Process-based restoration is particularly impor- Material deposited in the wetland was derived from both the
<br /> tant for watersheds such as the one discussed in this paper, hillslope and from eroded valley-bottom sediments.The National
<br /> which is subject to relatively frequent intense disturbances Park Service plans to restore channels, riparian areas, and
<br /> in the form of debris flows. As in the Uvas Creek example, wetlands impacted by the debris flow. Understanding HRV
<br /> attempts to 'permanently' impose a form that represents only of disturbance regimes provides context for the 2003 debris
<br /> one variant of a continually changing process-form continuum flow and restoration of the Lulu City wetland. Results were
<br /> are unlikely to succeed. used to assess the usefulness of active restoration.
<br /> HRV in river systems can be(1)extrapolated from theoretical
<br /> or empirical models (either conceptual or quantitative) of
<br /> process—form interactions in general, (2) based on historical Study Area
<br /> records from the study site,or(3)extrapolated from nearby,less
<br /> impacted, reference sites. Because no single method compre- The study area is the headwaters of the Colorado River on the
<br /> hensively describes historical conditions, a combination of west side of Rocky Mountain National Park,with particular fo-
<br /> approaches should be used when possible. Aerial photos, cus on the Lulu City wetland and the —29 km2 upstream
<br /> discharge and sediment gage records, specific gage analysis, (Figure 1).The elevation of the watershed ranges from —2830m
<br /> surveys, and dating modern deposits with dendrochronology at the Lulu City wetland, to 3944m at Mount Richthofen. The
<br /> are the most common methods to provide a historical context watershed is bounded by the Never Summer Mountains on the
<br /> for restoration (Soar and Thorne, 2000;Watson et al., 2007). west, La Poudre Pass on the Continental Divide to the north,
<br /> Typically,the aforementioned methods are capable of catego- and the Front Range of the Rocky Mountains to the east. The
<br /> rizing impacts to channel form and process for a time-scale on Never Summer Mountains consist primarily of Oligocene granite,
<br /> the order of 10'years. Given the short time-periods covered and the Front Range is primarily Proterozoic biotite schist with
<br /> by 'historical' investigations, restoration targets commonly some Oligocene rhyolitic flows and tuff(Braddock and Cole,
<br /> seek to emulate pre-disturbance or reference forms.However, 1990).Debris flows occur in the area as a result of steep slopes
<br /> periods that are long enough to include several major dis- along the main valley and are particularly prevalent in weath-
<br /> turbance events,typically 102 to 103 years,are probably nec- ered zones of hydrothermally altered bedrock (Sanford, 2010).
<br /> essary to categorize the dynamic nature of landscapes(Turner A debris fan from the eastern valley wall forms a constriction
<br /> rr _
<br /> Failure
<br /> i
<br /> Grand
<br /> Ditch
<br /> Lulu City
<br /> Legend Wetland
<br /> Roads
<br /> �!RMNP Border
<br /> Rocky Mountain Colorado
<br /> National Park River
<br /> 40.45°N,105.83°W N
<br /> 2005
<br /> 0 0.3 0.6 km
<br /> I I i
<br /> Figure 1. The project area is the upper Colorado River in Northern Colorado on the west side of Rocky Mountain National Park,USA.White arrows
<br /> indicate direction of water flow.Tributaries that flow into the Colorado River are diverted out of the basin to the north by the Grand Ditch(northward
<br /> pointing white arrow).
<br /> i
<br /> Copyright©2011 John Wiley&Sons,Ltd. Earth Surf.Process.Landforms,Vol.37,209-222(2012)
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