Bridging the Gaps: Wood Across Time & Space in Diverse...
Transcript of Bridging the Gaps: Wood Across Time & Space in Diverse...
Bridging the Gaps:Wood Across Time & Space
in Diverse Rivers
Ellen WohlColorado State University
Goal: For a river reach anywhere in the world, quantitatively predict
So, what are the knowledge gaps that keep us from doing this?
3) geomorphic & ecological effects of wood
1) all aspects of wood budget (Inputs, Storage, Outputs)
2) fluctuations in all parameters through time & space
I. Wood Budget:Components of Geomorphic & Biotic Context
forest dynamics
hillslope dynamics
channel dynamicsvalley-bottom dynamics
network (tributary) dynamics
biota (beaver)
Forest dynamics Stand characteristics (spatial density, tree age & size, species composition)Mortality (individual, mass – fire, insects, windstorm)
Hillslope dynamics Mass movements (debris flows, landslides, avalanches) that recruit trees
Channel dynamics
Valley-bottom dynamics
Network dynamics Tributary inputs of wood, water, sediment
Floodplain storage of wood, water, sediment
Wood transport, bank erosion, water & sediment discharges
Biota (beavers)
Wood recruitment & stabilization, formation of secondary channels
Components of Wood Budget
Qo
Qi
LoLi
D
S
ΔS =[Li – Lo + Qi/Δx – Qo/Δx – D + B] Δt
B
Benda & Sias, 2003
Li = Im + If + Ibe + Is + Ie
chronicforest mortality
tree topple,fire &windstorm
exhumationof buriedwood
massmovements
bankerosion
Benda & Sias, 2003
Early numerical simulations focused on recruitment (Beechie et al., 2000; Bragg, 2000; Welty et al., 2002; Gregory et al., 2003)
Knowledge gap:Diverse models have end prediction of storage, but need much more
region-specific calibration & testingNeed more effective consideration of how stable wood influences
wood in transport or how multiple pieces affect individual/collectivemobility
More recent models focus on
• forces acting on wood (Merten et al., 2010; Rafferty, 2013)
• stochastic prediction of wood load (Eaton et al., 2012)
• wood loads & related physical processes (Lancaster et al. 2003)
North St. Vrain Creek
0 500 1000 1500 2000 2500 3000 3500 4000 4500 5000 5500 6000 6500 7000 7500 8000 8500 9000
Wood load (
m3/h
a)
0
100
200
300
400
500
600
700
gorge
avg 49
fan avg 405
alternating anastomosing & small gorges
avg 79
anastomosingavg 192
occasional anastomosing
avg 85
single channel
avg 13
North St. Vrain jams
Cumulative distance downstream (m)
0 500 1000 1500 2000 2500 3000 3500 4000 4500 5000 5500 6000 6500 7000 7500 8000 8500 9000
Volu
me o
f w
ood in jam
(m
3)
0
2
4
6
8
10
12
14
16
avg 0.3
avg 1.1
avg 1.5
avg 0.8
avg 1.4avg 0.2
Wohl & Cadol, 2011
Cumulative distance downstream (m)
North St. Vrain Creek, Colorado, USA
singlechannel
singlechannel
alternating single & multiple channelsmultiplechannels
II. Temporal & spatial fluctuations: space
ΔSc = [Li – L0 + Qi/Δx – Q0/Δx – D + B]Δt
Li = Im + If + Ibe + Is + Ie
ΔSc = [Li – L0 + Qi/Δx – Q0/Δx – D + B]ΔtLi = Im + If + Ibe + Is + Ie
ΔSc = [Li – L0 + Qi/Δx – Q0/Δx – D + B]ΔtLi = Im + If + Ibe + Is + Ie
confined headwaters
unconfined headwaters
lower basin
Wohl, 2011a
Abbe & Montgomery, 2003
recruitmentmechanism
typical position inchannel networkIN-SITU COMBINATION TRANSPORT
landsliding
bank erosion
low order, steep
2nd – 4th order0.02 < S < 0.20
> 3rd orderS < 0.03
large alluvial channelsS < 0.01
Obliquelog steps
Bankinput
Orthogonallog steps
Valley
FlowDeflection
BarApex
Meander
Rafts
bench
alterschannel
alterschannel
alterschannel
noeffect
noeffect
noeffect
widecontinuous
moderatecontinuous
widecontinuous
narrowdiscontinuous
Longitudinal & lateral extent of floodplainWohl, 2014
Knowledge gap:Within a region, lack of data on downstream trends in wood load in
unaltered rivers with drainage areas exceeding ~ 300 km2
(Fox & Bolton, 2007)
Knowledge gap:Between regions, limited data for full climatic-biotic range in temperatezone, & very limited data for tropics & boreal zones
CR = La Selva, Costa Rica WA1= Western WashingtonWA2 = Western Washington WA3 = Cascade Range, WAOR1 = Western OregonOR2 = Coast Range, Oregon
AK = Southeast AlaskaBC = SW British ColumbiaMI = Northern MichiganCO1 = Front Range, ColoradoCO2 = Front Range, ColoradoWY1 = Bighorn Range, Wyoming
WY2 = Absaroka Range, WYWY3 = Bridger-Teton NF, WYSA = Southern Andes, ChileTF = Tierra del Fuego, ArgentinaAU = Southeast AustraliaNZ = South Island, New Zealand
Cadol et al., 2009
Pacific Northwest Southern Rockies
boreal
temperate
tropical
low, transient wood loads (rapid decay, mobile)
(Wohl et al., 2012)
wood highly variable between sites
??? maybe moderateto high wood loads
Locations of field studies on instream wood published in English-language journals
Arctic circle
Tropic of Cancer
Tropic of Capricorn
Relative dearth of studies in high and low latitudes
East St. Louis Creek
left bank
flow
0
10 m
10 m1996
left bank
flow
0
10 m2006
19961997199819992000200120022003200420052006
Wohl & Goode, 2008
Measured short-term fluctuations
Temporal fluctuations
Channel-spanning logjams in Rocky Mountain National Park, USA
2010
Days since 1 May
0 50 100 150
Dis
ch
arg
e (
m3
/s)
0
5
10
15
20
25
2011
Days since 1 May
0 50 100 150D
isch
arg
e (
m3
/s)
0
5
10
15
20
25
2012
Days since 1 May
0 50 100 150
Dis
ch
arg
e (
m3
/s)
0
5
10
15
20
25
2013
Days since 1 May
0 50 100 150
Dis
ch
arg
e (
m3
/s)
0
5
10
15
20
25
2014
Days since 1 May
0 50 100 150
Dis
ch
arg
e (
m3
/s)
0
5
10
15
20
25
Year
2010 2011 2012 2013 2014
Nu
mber
of ja
ms
0
20
40
60
80
100
120
140
NSV
Ouzel
Cony
Hunters
blowdown flood
high, short peak high, long peak no peak autumn flood normal year
Wohl, 2011a
0
50
0
100 200 300 400
100
150
200
250
Time (years)
Longer term fluctuations in wood load on forest floorColorado Front Range
Knowledge gap:Relatively little published on temporal fluctuations of wood withina river segment or drainage basin, & particularly for unmanagedrivers (e.g., Gurnell & Sweet, 1998 & Lassettre et al., 2008 for managed rivers)
III. Geomorphic & ecological effects of wood: geomorphic
• reach-scale within channel• hydraulics & local scour (Shields & Smith, 1992; Mutz, 2003)
• sediment transport (Brooks et al., 2003)
• forced alluvial bed (Montgomery et al., 1996)
• wood, vegetation & planform (Gurnell et al., 2012)
• reach-scale across valley bottom• log jams & avulsions (Phillips, 2012)
• multi-thread channels (Wohl, 2011b) & floodplain large wood cycle (Collins et al., 2012)
Meandering
Anastomosing
Braided
Forestchronosequence
Abandoned channel/oxbow
Ephemeral patches ofpioneer vegetation
Channel
In-channelwood jam
Mature forestpatches
Buriedwood jam“hardpoint”
Secondary channel
Frequently-shifting channels
Avulsionaroundhardpoints
Migrationbetweenhardpoints
Channel migration
Collins et al., 2012
Knowledge gaps:
• quantifying flow resistance & obstruction –numerous case studies in field & flumes (e.g., Young, 1991;
Shields & Gippel, 1995; Dudley et al., 1998; Manga & Kirchner, 2000; Wallerstein et al., 2001; Curran & Wohl, 2003; Hygelund & Manga, 2003; Wilcox & Wohl, 2006; Wilcox et al., 2006; Daniels & Rhoads, 2007;
Manners et al., 2007) –but no widely applicable formula or technique
Knowledge gaps:
• quantifying sediment storage –numerous case studies (e.g., Megahan, 1982; Klein et al., 1987;
Bugosh & Custer, 1989; Nakamura & Swanson, 1993; Smith et al., 1993; Thompson, 1995; Hart, 2002; Haschenburger & Rice, 2004; Fisher et al., 2010;
Ryan et al., 2014) & numerical models for particular river systems(e.g., Lancaster et al., 2003; Eaton et al., 2012)
• no broadly applicable conceptual model
Drainage area (km2)
Sto
red
sed
imen
t p
er
un
it a
rea
of
chan
ne
ljammed steps &
sediment wedges
dispersedwood & sediment
wood rafts &floodplain sediment
Drainage area (km2)
0 50 100 150 200
Sedim
ent
volu
me (
m3/h
a)
0
1000
2000
3000
4000
5000
6000
other
jammed steps
Wohl & Scott (in review)
Spearman correlation coefficient = 0.89
102 104
Knowledge gaps:
• documentation of potential alternative stable stables • wood-rich vs wood-poor (Wohl & Beckman, 2014)
• high vs diminished biogeomorphic complexity of floodplain(Collins et al., 2012)
• linear vs threshold effects of wood load (e.g., Wohl, 2011b; Beckman & Wohl, 2014a)
• potential for emergent properties (e.g., anastomosing channels)
• effects of dramatic historical reductions in wood loads
Ecological effects
• reach-scale within channel• habitat abundance & diversity
(Carlson et al., 1990; Richmond & Fausch, 1995)
• enhanced nutrient storage & uptake (Buckley & Triska, 1978; Ward & Aumen, 1986; Beckman & Wohl, 2014b)
• greater biomass (Gowan & Fausch, 1996; Nagayama et al., 2012)
• reach-scale across valley bottom• floodplain habitat abundance & diversity (Harmon et al., 1986)
• floodplain nutrient storage & uptake (Naiman et al., 2010)
• floodplain biomass (Benke, 2001)
Ongoing “Leaky Rivers” project research indicates greater wood loads& measures of physical complexity are associated with
greater nutrient uptakegreater insect predator (fish, riparian spiders) biomass & diversity
Knowledge gaps:
• linear versus threshold effects for habitat, diversity, and/or biomass
• is wood ecologically important where transient (tropics)?
• potential for emergent properties
• effects of dramatic historical reductions in wood loads
Additional knowledge gaps
• effective level of instream wood to create desired environmentaleffects (e.g., linear or threshold?) – ELJs (Abbe & Brooks, 2011; Gallisdorfer et al., 2014)
• big rivers
• most areas outside of Pacific Northwest
• effect of wood loads on wood transport (we have a start with existing
numerical models (Eaton, Lancaster) & flume studies (Braudrick & Grant, 2000, 2001; Bocchiola et al., 2006)
• temporal variation (HRV or NRV)
• how to effectively reintroduce/manage wood
• education/outreach for river restoration & management to counternegative perceptions (Chin et al., 2008)
For a river reach anywhere in the world, quantitatively predict
• all aspects of wood budget (I, S, O)• fluctuations through time & space• geomorphic & ecological effects of wood
Need • more case studies from diverse environments
• syntheses, meta-data, conceptual models, & numerical simulations for
hydraulicssediment dynamicschannel & floodplain morphologyecological effects (habitat, nutrients, thresholds leading to
alternative stable states)
• education & outreach on benefits of wood
how much?stable? mobile?
effects: linear, threshold?
fluctuations through time?
time
time
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