220 • Z.RUBIN ETAL.
<br /> recent Grand Ditch-caused debris flows.Comparing the rate of overbank deposition on the west side of the valley,the recent
<br /> recent deposition with the historic rate of preservation is of shift is not outside the HRV of aggradational processes.
<br /> limited usefulness. Furthermore,as deposits to the head of the Although debris-flow deposits are spatially heterogeneous in
<br /> wetland increase the valley gradient, the aggradation itself the wetland, making generalization difficult,the 2003 deposit
<br /> should lead to greater transport capacity and a potential is not unusually large in either thickness or spatial extent when
<br /> mechanism for reducing sediment preservation rates. As compared with other deposits of the past two centuries or
<br /> mentioned previously, for more than 3000 years the eastern when compared with pre-settlement deposits of the past four
<br /> portion of the wetland has aggraded almost exclusively from millennia. The southernmost extent of the 2003 deposit was
<br /> peat production and overbank deposition without any fluvial near Pit 28 (Figure 2). Near-surface deposits at Long W @150
<br /> reworking or channel migration into the region,whereas the and SW Hole are –60 and –150m further south, respectively,
<br /> west side of the wetland has filled primarily through debris and were therefore probably deposited by larger,pre-2003 events.
<br /> flows and overbank deposition. The uniform, horizontal Similarly, coarser deposits and deposits equal to or thicker than
<br /> reflections in the GPR sections XS2–XS5 (Figure 4) indicate the 2003 debris-flow deposit are visible in the majority of holes
<br /> that the preserved deposits are from peat and overbank in the west side of the wetland.The increased rate of aggradation
<br /> deposition, and the absence of fluvial reworking of sediments in the Lulu City wetland is therefore attributed to increased
<br /> suggests that the aggradation has been purely depositional. debris-flow frequency not increased magnitude.
<br /> Interestingly,although the east and west sides of the wetland Restoration projects are inherently driven by cultural pre-
<br /> have been dominated by different processes, over the past ferences. What species we seek to protect, which locations
<br /> 3000+ years aggradation has occurred at roughly the same merit restoration, and project designs are all guided by
<br /> rates(Figure 8).This suggests that the wetland topography is cultural, political, and aesthetic values. These biases are
<br /> in a state of dynamic adjustment. Aggradation in the west not inherently problematic, but we believe restoration is
<br /> might disconnect the floodplain from the channel and thus most effective when guided by a clear picture of how land-
<br /> overbank deposits would be confined to the east. Peat scapes undisturbed by human activities function. HRV high-
<br /> production in the east may similarly elevate and disconnect the lights these processes by demonstrating the variability of
<br /> eastern side of the valley bottom from the river, encouraging dynamic and changing landscapes. Furthermore, by recog-
<br /> overbank deposition in the west.Similar equilibrium adjustments nizing the range of historic variability, we also become
<br /> may also occur longitudinally.Deposition at the head of the wet- aware of future variability.A landscape manager is then able
<br /> land increases the channel slope and facilitates reworking of those to interpret contemporary monitoring data within a broader
<br /> deposits and/or deposition farther downstream.The dichotomy of narrative. In the case of the Lulu City wetland restoration,
<br /> aggradational processes on the east and west sides of the valley we are left to ponder new questions such as: is a short-term
<br /> suggests deposits will be preserved. Because east and west have increase over long-term aggradation rates problematic, and
<br /> aggraded at similar rates historically and recent aggradation rates what restoration measures can be applied to recover funda-
<br /> are of a similar magnitude throughout the radiocarbon-dated mental processes such as preventing future debris flows from
<br /> profiles in the wetland,we expect the east side will continue to initiating along Grand Ditch?
<br /> be purely depositional and that the recent debris-flow deposits will The key information gained from our characterization of this
<br /> persist. Modern aggradation rates can thus be compared with study site is that(i)the Lulu City wetland has been aggrading for
<br /> historic rates without introducing bias. several millennia, and the aggradation rate of the past 1-2
<br /> centuries is substantially higher than long-term pre-settlement
<br /> averages, although short-term pre-settlement aggradation rates
<br /> Conclusions of the past may have been similar to recent times, (ii) valley
<br /> aggradation has occurred at similar rates on east and west sides
<br /> Aggradation rates were variable through the late Holocene, of the Lulu City wetland, and (iii) depositional processes and
<br /> perhaps as a reflection of climatically driven changes in sediment soil textures on both sides of the wetland are within HRV.We
<br /> yield,valley-bottom depositional processes,and peat production interpret the similar rates of aggradation on east and west sides
<br /> rates. The Grand Ditch and earlier land-use changes (mining, of the wetland, and the similarity of pre-settlement and post-
<br /> beaver trapping,timber harvesting,human-ignited fires,etc.)have settlement depositional processes and sediments, to suggest
<br /> altered the rate of deposition beyond long-term average rates that the wetland is capable of adapting to the recent debris-flow
<br /> prior to Euro-American settlement of the region.Inferred rates of deposition. These findings suggest that intensive restoration
<br /> aggradation range from 4-20 cm/100 yr from –4250 yr BP until measures and hard engineering structures are not needed and
<br /> –200 yr BP. The 160years between 4089 and 4249 yr BP potential benefits of intensive restoration are likely outweighed
<br /> aggraded at 20 cm/100 yr,or half the rate of the last 1-2 centuries, by the disturbance of heavy equipment. However, it is impor-
<br /> suggesting that some pre-settlement periods were comparable tant to limit anthropogenic debris-flow sediment from entering
<br /> with recent aggradation rates. the wetland to ensure its long-term function and maintenance.
<br /> In general, rates are spatially consistent throughout the Lulu
<br /> City wetland. Similarly, modern rates (-45cm/100yr) of the Acknowledgements—We thank Rocky Mountain National Park for
<br /> past approximately two centuries are consistent throughout financial, logistical, and informational support. The final manuscript
<br /> the wetland and approximately six times higher than historic benefited greatly from the thoughtful comments of Frederick J.Swanson,
<br /> long-term average rates.The east side of the wetland has been Stuart Lane,and an anonymous reviewer.
<br /> stable for 3000+years with peat accumulation and overbank
<br /> deposition as the dominant processes of fill. Deposits are
<br /> therefore expected to be persistent features of the landscape.
<br /> Peat was present in the west(SW Hole and Long W @150 m), References
<br /> the top of which was dated at roughly the time of human Baker GS,Jordan TE,Pardy J.2007.An introduction to ground penetrating
<br /> impacts (-130yr BP). Land-use and Grand Ditch sediment radar(GPR). Geological Society of America Special Papers 432:
<br /> inputs shifted the mechanisms of fill in the west side from peat 1_18,
<br /> accumulation to processes of sedimentation. However, since Beres M Jr, Haeni FP. 1991. Application of ground-penetrating-radar
<br /> long-term aggradation was primarily through debris flows and methods in hydrogeologic studies.Ground Water 29:375-386.
<br /> Copyright 0 2011 John Wiley&Sons,Ltd. Earth Surf.Process.Landforms,Vol.37,209-222(2012)
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