a consortium of catchment - university of western ontario · 2013. 8. 29. · pet/p 1974 - 1979...
TRANSCRIPT
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A consortium of catchment scientists, including: Adam Spargo USA Mary Beth Adams (FER) John Campbell (HBR) Alan Covich (LUQ) David Clow (LVW) Clifford Dahm (SEV) Kelly Elder (FRA) Nancy Grimm (CAP) Julia Jones (AND) Stephen Sebestyen (MAR) James Vose (CWT) Mark Williams (NWT) Canada Fred Beall (TLW) Tom Clair (KEJ) John Pomeroy (MRM) Patricia Ramlal (ELA) Rita Winkler (UPC) Huaxia Yao (DOR)
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Rationale
3
0 These watershed studies are unique.
0 Represent longest existing paired records of climate and hydrology.
0 Provide opportunity to explore effects of climate on water yields in headwaters of the US and Canada.
0 Collective potential of these studies is only beginning to be realized.
Coweeta Experimental Forest and LTER, North Carolina (CWT)
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Motivation Why are we interested in the Budyko curve?
The Budyko Curve provides a reference condition for the water balance.
If we assume it depicts the expected partitioning of P into Q, then we can begin to account for the reasons why sites vary from the curve.
Russian climatologist 1920 –2001
Jones et al. 2011. Ecosystem processes and human influences regulate streamflow response to climate change at long-term ecological research sites . Bioscience Under Review
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Breaking down the Budyko Curve
5
Water limit: AET = P. A site cannot plot above the blue line unless there is an additional input of water beyond precipitation.
Energy limit: AET = PET. A site cannot plot above the red line unless precipitation is being lost (e.g., water lost to groundwater system).
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What do deviations from the Budyko curve mean?
HORIZONTAL deviations change in the climatic conditions
6
Warmer, drier
Le
ss r
un
off
VERTICAL deviations change in partitioning
between ET and Q
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Question 1 Do average annual values for
reference catchments fall on the Budyko curve?
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“LTER” Sites (including US LTER, USGS, USFS and Cdn sites)
8
0 30 sites across North America selected based on
0 Reference catchments
0 Coverage of major biomes
0 Coverage of major climate regions
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“LTER” Sites (including US LTER, USGS, USFS and Cdn sites)
9
0 30 sites across North America selected based on
0 Reference catchments
0 Coverage of major biomes
0 Coverage of major climate regions
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Record length - matched P, T, Q Long-term matching climate and flow records from
US clim/hydroDB website (http://www.fsl.orst.edu/climhy/) Cdn HELP website (http://www.canforhydro.org/)
Ca
tch
me
nt
are
a (
ha
)
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Theoretical vs. observed distribution of study sites relative to the Budyko Curve
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Accuracy of Budyko in predicting long-term (10-yr) average discharge
y = 1.055xR² = 0.5953
y = 1.1321xR² = 0.6922
0
500
1000
1500
0 500 1000 1500O
bse
rved
AET
(P
-Q
)
Predicted AET using Budyko
LUQ
Line of best fit
Line with LUQ removed
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Hurricane Hugo hit the site in September 1989 reducing above ground biomass by 50%.
0.0
0.1
0.2
0.3
0.4
0.5
0.6
0.0 0.2 0.4 0.6 0.8
AET
/P
PET/P
1988 - 1989 (pre huricane)
1990 - 1995 (1- 5 yrs post Hugo)
1996 - 2005 (6 -10 yrs post Hugo)
Luquillo Experimental Forest, LTER site, and USGS WEBB site, Puerto Rico (LUQ)
y = 1.055xR² = 0.5953
y = 1.1321xR² = 0.6922
0
500
1000
1500
0 500 1000 1500
Ob
serv
ed A
ET (
P -
Q)
Predicted AET using Budyko
LUQ
Line of best fit
Line with LUQ removed
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Maximum deviation of the longterm average Evaporative index from the Budyko Curve for each of
the 30 study sites
Whilst the Evaporative Index for the 30 sites generally follows the Budyko curve there remains a lot of deviation.
Why does this occur?
-0.30
-0.20
-0.10
0.00
0.10
0.20
0.30
0.40
HB
RA
ND
FER
TLW
MA
RN
TLO
LYC
AS
ELA
DO
RSB
CK
EJM
RM
MA
YK
BS
PIE
TEN
CW
TU
PC
GC
EN
WT
CA
RK
NZ
BN
ZB
ESSE
VLU
QFR
ALV
WC
AP
AR
C
Lon
gte
rm A
vera
ge A
ET/P
de
viat
ion
th
e
Bu
dyk
o
14
0 ARTIFACT?
0 ET=P-Q
0 Timing of P vs. ET over the year
0 Inadequate measures of P, ET, Q
0 Missing measures of other components of the water balance (i.e., groundwater gains or losses?)
0 REAL?
0 Natural disturbance legacy effects
0 Vegetation, topography, and soils may modify water balance
0 Ecosystem may acclimate/adapt to climate change
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Whilst the Evaporative Index for the 30 sites generally follows the Budyko curve there remains a lot of deviation.
Why does this occur?
15
0 ARTIFACT?
0 ET=P-Q
0 Timing of P vs. ET over the year
0 Inadequate measures of P, ET, Q
0 Missing measures of other components of the water balance (i.e., groundwater gains or losses?)
0 REAL?
0 Vegetation, topography, and soils may modify water balance
0 Ecosystem may acclimate/adapt to climate change
ET underestimated
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Whilst the Evaporative Index for the 30 sites generally follows the Budyko curve there remains a lot of deviation.
Why does this occur?
16
0 ARTIFACT?
0 ET=P-Q
0 Timing of P vs. ET over the year
0 Inadequate measures of P, ET, Q
0 Missing measures of other components of the water balance (i.e., groundwater gains or losses?)
0 REAL?
0 Vegetation, topography, and soils may modify water balance
0 Ecosystem may acclimate/adapt to climate change
Gro
un
dw
ate
r lo
ss
un
de
rest
ima
ted
? Can we use the Budyko curve to identify where we have confidence in closing the water budget? What are our gaps in knowledge?
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Question 2 Do year-to-year deviations in the evaporative index
provide insight into the responsivity (resistance) and elasticity (resilience) of catchment water yields
to changing climatic conditions?
17
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Spider plots showing year-to-year deviations from long term average
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Spider plots showing year-to-year deviations from long term average
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Water Yield Metrics RESPONSIVITY is the degree to which runoff (Q) is synchronized with precipitation (P), and is measured from the deviation in the Evaporative Index (i.e., Δy-axis).
20 Carey et al. 2010. Inter-comparison of hydro-climatic regimes across northern catchments: synchronicity, resistance and resilience. Hydrol. Process. (2010)
Eva
po
rati
ve in
dex
(A
ET
/P)
Dryness Index (PET/P) Dryness Index (PET/P)
HIGH responsivity (or resistance); water yields are expected as P is transferred to Q (synchronous)
LOW responsivity (or resistance); water yields are higher or lower than expected (not synchronous)
Metrics defined for reference
conditions
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0.0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9M
axim
um
Inte
ran
nu
al D
evia
tio
n in
AET
/P
No
rmal
ise
d t
o t
he
Bu
dyk
o C
urv
e
Rank ordering of amplitude of year-to-year deviation in Evaporative index (normalized to the Budyko Curve)
21
LOWER responsivity
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0.0
0.2
0.4
0.6
0.8
1.0
1.2
0.00 0.20 0.40 0.60 0.80 1.000.0
0.2
0.4
0.6
0.8
1.0
1.2
0.0 0.2 0.4 0.6 0.8 1.00.0
0.2
0.4
0.6
0.8
1.0
1.2
0.0 0.2 0.4 0.6 0.8 1.0
0.0
0.2
0.4
0.6
0.8
1.0
1.2
0.0 0.2 0.4 0.6 0.8 1.0
0.0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9M
axim
um
Inte
ran
nu
al D
evia
tio
n in
AET
/P
No
rmal
ise
d t
o t
he
Bu
dyk
o C
urv
e
Rank ordering of amplitude of year-to-year deviation in Evaporative index (normalized to the Budyko Curve)
22
LOWER responsivity
22 Fraser Andrews Niwot Coweeta
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R² = 0.4509
0
100
200
300
400
500
600
700
0 200 400 600 800 1000
An
nu
al
Dis
ch
arg
e (
mm
)
Annual Precipitation (mm)
0.0
0.2
0.4
0.6
0.8
1.0
1.2
0.00 0.20 0.40 0.60 0.80 1.00
R² = 0.9726
0
500
1000
1500
2000
2500
0 500 1000 1500 2000 2500 3000 3500
An
nu
al
Dis
ch
arg
e (
mm
)
Annual Precipitation (mm)
R² = 0.2956
0
200
400
600
800
1000
1200
0 500 1000 1500 2000
An
nu
al
Dis
ch
arg
e (
mm
)
Annual Precipitation (mm)
Andrews
Niwot
0.0
0.2
0.4
0.6
0.8
1.0
1.2
0.0 0.2 0.4 0.6 0.8 1.0
0.0
0.2
0.4
0.6
0.8
1.0
1.2
0.0 0.2 0.4 0.6 0.8 1.0
R² = 0.7645
0
200
400
600
800
1000
1200
1400
1600
0 500 1000 1500 2000 2500
An
nu
al
Dis
ch
arg
e (
mm
)
Annual Precipitation (mm)
Fraser
23
Cowetta
0.0
0.2
0.4
0.6
0.8
1.0
1.2
0.0 0.2 0.4 0.6 0.8 1.0
Associations between year-to-year deviations (inset) and P vs. Q coupling)
Responsivity=0.12
Responsivity=0.64 Responsivity=0.41
Responsivity=0.37
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0.0
0.2
0.4
0.6
0.8
1.0
0.0 0.2 0.4 0.6 0.8 1.0
AET
/P
PET/P
Budyko
Can we identify sites where ecosystems are undergoing fundamental changes in response to climatic conditions?
Responsivity=0.19
Caspar (California, USA)
0.0
0.2
0.4
0.6
0.8
1.0
1990 1992 1994 1996 1998 2000 2002 2004
Ru
no
ff R
ati
o
0
100
200
300
400
500
600
700
800
0
500
1000
1500
2000
2500
1990 1993 1996 1999 2002
PET
(m
m)
Pre
cip
itat
ion
, Dis
char
ge (
mm
) Precipitation Discharge PET
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-0.1
0.0
0.1
0.2
0.3
0.4
0.5
0.0 0.1 0.2 0.3 0.4 0.5 0.6
AET
/P
PET/P
1974 - 1979
1980 - 1989
1990 - 1995
Budyko
Carnation Creek (British Columbia, Canada)
560
600
640
680
720
760
800
0
500
1000
1500
2000
2500
3000
3500
4000
4500
1974 1977 1980 1983 1986 1989 1992 1995
PET
(m
m)
Pre
cip
itat
ion
, Dis
char
ge (m
m)
Precipitation
Discharge
PET
0.0
0.2
0.4
0.6
0.8
1.0
1.2
1974 1977 1980 1983 1986 1989 1992 1995
Ru
no
ff R
atio
Responsivity=0.42
Can we identify sites where ecosystems are undergoing fundamental changes in response to climatic conditions?
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0.0
0.2
0.4
0.6
0.8
1.0
1.2
1.4
1994 1997 2000 2003 2006 2009
Run
off R
atio
-0.4
-0.2
0.0
0.2
0.4
0.6
0.8
0.0 0.2 0.4 0.6 0.8
AET
/P
PET/P
1994 - 19992000 - 20072008 - 2009Budyko
0
50
100
150
200
250
300
0
200
400
600
800
1000
1200
1400
1994 1997 2000 2003 2006 2009
PET
(m
m)
Pre
cip
itat
ion
, Dis
char
ge (m
m)
Precipitation Discharge PET
Loch Vale (Colorado, USA)
!
Responsivity=0.72
Can we identify sites where ecosystems are undergoing fundamental changes in response to climatic conditions?
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Question 3 Does elasticity lead to shorter recovery times (return to
pre-disturbance water yield) following disturbance?
27
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28
Water Yield Metrics ELASTICITY is the degree to which a catchment can return to normal functioning following perturbations, and is measured as the ratio of deviations in dryness index to evaporative index (i.e., Δx-axis/Δy-axis).
Dryness Index (PET/P)
LOW elasticity (<1) is the result of small horizontal range relative to vertical range
Dryness Index (PET/P)
HIGH elasticity (>1) is the result of large horizontal range relative to vertical range
Eva
po
rati
ve in
dex
(A
ET
/P)
Eva
po
rati
ve in
dex
(A
ET
/P)
Carey et al. 2010. Inter-comparison of hydro-climatic regimes across northern catchments: synchronicity, resistance and resilience. Hydrol. Process. (2010)
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Responsivity does not imply elasticity
29
y = -2.2806x + 2.0876 R² = 0.2701
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
0.0 0.2 0.4 0.6 0.8 1.0
Ela
stic
ity
Responsivity
y = -2.2806x + 2.0876 R² = 0.2701
0.0
2.0
4.0
6.0
8.0
10.0
12.0
14.0
0.0 0.2 0.4 0.6 0.8 1.0
Ela
stic
ity
Responsivity
0.1
1.0
10.0
Max
imu
m In
tera
nn
ual
Dev
iati
on
in A
ET/P
N
orm
alis
ed
to
th
e B
ud
yko
Cu
rve
Responsivity
Elasticity
10 1 0.1
Max
imu
m i
nte
ran
nu
al
dev
iati
on
in
AE
T/P
10 1 0.1 M
axim
um
in
tera
nn
ual
d
evia
tio
n i
n P
ET
/P /
AE
T/P
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Study Area HJ Andrews Hubbard Marcel
Location Oregon New Hampshire Minnesota
Treated Watershed WS01 WS2 S6
Control Watershed WS02 WS3 S2
Cut (year/percent) 1963 / 100% 1964 / 100% 1980 / 87%
Data period pre cut 5 years 7 years 13 years
Data period post cut 47 years 43 years 27 years
Vegetation Type Coniferous Deciduous Deciduous
Demonstration of elasticity vs. recovery following disturbance using paired catchment studies
30
Site selection criteria: 1. Pre and post disturbance data available
2. Similar disturbance (100% cut)
Marcell (MAR)
Hubbard (HUB)
HJ Andrews (HJA)
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Study Sites HJA HUB MAR
Treated Watershed
WS01 WS2 S6
Vertical Variation (V)
0.08 0.18 0.37
Horizontal Variation (H)
0.03 0.24 0.54
Ratio of Horizontal to Vertical (H/V)
0.38 1.36 1.46 0.0
0.2
0.4
0.6
0.8
1.0
0.0 0.2 0.4 0.6 0.8 1.0
Evap
ora
tive
Ind
ex (
AET
/P
Dryness Index (PET/P)
0.0
0.2
0.4
0.6
0.8
1.0
0.0 0.2 0.4 0.6 0.8 1.0
Evap
ora
tive
Ind
ex (
AET
/P
Dryness Index (PET/P)
0.0
0.2
0.4
0.6
0.8
1.0
0.0 0.2 0.4 0.6 0.8 1.0
Evap
ora
tive
Ind
ex (
AET
/P
Dryness Index (PET/P)
HJ Andrews – WS01
Hubbard – WS2
Marcell – S6
31
Elasticity metrics for study sites
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Study Sites HJA HUB MAR
Treated Watershed
WS01 WS2 S6
Vertical Variation (V)
0.08 0.18 0.37
Horizontal Variation (H)
0.03 0.24 0.54
Ratio of Horizontal to Vertical (H/V)
0.38 1.36 1.46 0.0
0.2
0.4
0.6
0.8
1.0
0.0 0.2 0.4 0.6 0.8 1.0
Evap
ora
tive
Ind
ex (
AET
/P
Dryness Index (PET/P)
0.0
0.2
0.4
0.6
0.8
1.0
0.0 0.2 0.4 0.6 0.8 1.0
Evap
ora
tive
Ind
ex (
AET
/P
Dryness Index (PET/P)
0.0
0.2
0.4
0.6
0.8
1.0
0.0 0.2 0.4 0.6 0.8 1.0
Evap
ora
tive
Ind
ex (
AET
/P
Dryness Index (PET/P)
HJ Andrews – WS01
Hubbard – WS2
Marcell – S6
32
Elasticity metrics for study sites
If elasticity is linked to time required to return to pre-disturbance water yields, then we expect HJ Andrews to have a long recovery.
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33
Elasticity metrics for study sites
Lower elasticity results in longer recovery times in water yields
following disturbance.
Study Site HJA HUB MAR
Treated Watershed
WS01 WS2 S6
Vertical Variation (V)
0.08 0.18 0.37
Horizontal Variation (H)
0.03 0.24 0.54
Ratio of Horizontal to Vertical (H/V)
0.38 1.36 1.46
-200
-100
0
100
200
300
400
500
600
195
3
1956
1959
1962
1965
1968
1971
1974
1977
1980
1983
1986
1989
1992
1995
1998
2001
2004
2007
Ob
serv
ed -
pre
dic
ted
dis
char
ge (
mm
)
HJ Andrews – WS01
Elasticity=0.38 Recovery=50+ yr
-200
-100
0
100
200
300
400
500
600
195
8
1961
1964
1967
1970
1973
1976
1979
1982
1985
1988
199
1
1994
1997
200
0
2003
2006
Ob
serv
ed -
pre
dic
ted
dis
char
ge (
mm
)
Hubbard – WS2
Elasticity=1.36 Recovery=10 yr
-200
-100
0
100
200
300
400
500
600
1965
1968
1971
197
4
1977
1980
1983
1986
1989
1992
1995
1998
2001
2004
Ob
serv
ed -
pre
dic
ted
dis
char
ge (
mm
)
Marcell – S6
Elasticity=1.46 Recovery=1 yr
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Summary Budyko curve described partitioning of P into ET and Q Deviations (average) provide insight into
0 Inaccurate or incomplete representation of water balance components (HJA, MAR)
0 Natural disturbances and their legacies (LUQ)
Deviations (year to year) provide insight into responsivity (resistance) and elasticity (resilience) of water yields to global change Future work will focus on:
0 Incorporating uncertainty estimates in water balances 0 Discriminating climate signal from natural or anthropogenic
disturbance effects 0 Exploring future scenarios and how they may result in changes in
water yields 0 Considering downstream consequences to water supplies
34
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Acknowledgements
0 “LTER Synthesis Workshops” funded by the LTER Network Office
0 NSF LTER grants to participating USA sites
0 USFS and USGS for initial establishment and continued support of watershed studies at many of the study sites
0 NCE-SFM funded project on HydroEcological Landscapes and Processes (HELP) and the participating Canadian sites
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Future Changes in Water
Fire Snow Outbreaks
Logging
Roads, landslides
Exurban expansion