cuahsi cyberseminar april 01, 11 · 2017-04-28 · climate forecasts and water management :...
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Climate Forecasts and Water Management :
Opportunities and Challenges
Sankar Arumugam Department of Civil & Environmental Engineering
North Carolina State University, Raleigh
CUAHSI Cyberseminar – April 01, 11
Presentation Outline
• Forecast Producers and Consumers
– Perspectives on Risk: Supply and Demand
• Dynamic Risk Management Framework
– Water Contracts with reliability of supply
• Insights from Retrospective Analyses
• Opportunities and Challenges
– Uncertainty Reduction
– Scope for Nutrient Allocation
Large Scale Hydroclimatology & Water Management
Hydroclimate Dynamics
Diagnosis
Physical Significance
Assimilation
Climatic Indices Land Surface Indices
Hydrologic Fluxes Estimation
Modeling
Forecasting
Water Management
System Design
Impact/Assessment
Allocation/Operation
Understanding &
Monitoring of Large
Scale Hydroclimatic
Systems
General Circulation Model
“Downscaling”
Regional Climate Model
Hydrologic Model
Exogenous Climate Predictors
Statistical Model
Forecasts of Reservoir Inflows and Flood Flows
Forecasting Seasonal Streamflow volumes – Two Approaches
Presentation Outline
• Forecast Producers and Consumers
– Perspectives on Risk: Supply and Demand
• Dynamic Risk Management Framework
– Water Contracts with reliability of supply
– Restriction Levels if forecasts go wrong
– Allocation Model conditioned on current storages
– Tariff, Compensation and Penalties
• Insights from Retrospective Analyses
• Opportunities and Challenges
Climate induced Risk on Water
• Forecast Producers
– Climate Scientists and Hydrologists
– Express seasonal streamflow uncertainty as
terciles or as ensembles
• Forecast Consumers
– Water Managers and Reservoir Operators
– Often risk averse; No reward for using forecasts
– Difficulty interpreting/relating forecasts to releases
– Often manages the system based on rule curves
(based on long-term operation)
– Need not quantify conditional risk
Attributing Climate Risk on Water Management
• Needs to be prognostic
• Relate water supply risk to demand risk
– Assigning reliability of supply for yield types
– Estimate reliability as part of allocation process
• Include compensations and penalties
– if forecasts go ‘wrong’ (false alarms or missed
targets)
• Tariff if specified yield is delivered
– Could act as an insurance scheme
• Limited Skill or Skill only in few seasons
– Include probabilistic constraint on storages
Presentation Outline
• Forecast Producers and Consumers
– Perspectives on Risk: Supply and Demand
• Dynamic Risk Management Framework
– Water Contracts with reliability of supply
– Restriction Levels if forecasts go wrong
– Allocation Model conditioned on current storages
– Tariff, Compensation and Penalties
• Insights from Retrospective Analyses
• Challenges and Way forward
Dynamic Water Allocation Model - Formulation
• Reservoir Inflow Forecasts Ensembles
• Water Contracts Specification
• Water Allocation Model for Bulk Sector
contracts
– Simulation – Optimization Model
Sankarasubramanian et al., WRR, 2009.
Water Contracts Specification
Specification Notation Illustration
Duration T 1 Year or 3 months
Release Ri, ith
use
5000 mm3 over T
Monthly Release Rti = bti bti = 1/12 if uniform
supply
Tariff (Value) i $1000
Contract
Reliability
(1-pfi) 90% for municipal use
What if Forecasts go Wrong?
Specification Notation Illustration
Restriction Wi* 500 hm3 - Industry
Restriction level j = 1, nl 1st– Lawn, Golf
2nd – Industry & above
Restriction
Fraction
aij 1st– 0 hm3; 2nd – 500
hm3
Compensation gij 1st– $100; 2nd – $300
Contract Failure vi $ 2500 if Wi > 500 hm3
Water Allocation Model • Modify the Allocation Rule – Maximize the
annual/seasonal net value from releases
conditioned on the forecasts
O =
– Ri – Release (Yield) for use ‘i’
– i - Unit value of water for delivery – Tariff function
– N – Number of uses (Contracts)
– Wil – Restriction at level ‘l’ with compensation gil
– i- Contract penalty if wi > wi*
*
1 1 1 1
( ) ( )l
i
nn n n
i i il il i i
i i j i
E R W W W g
Objective Function:
Maximize the net value from contracts and surplus water provision
Subject to
•P(Wi Wi*) pfi - Contract Level Constraint
For Industry, at a reliability (1-pfi) = 90%, P(Wi 500) 0.10
•P(STST*) ps - End of the Year Storage Constraint
For ST* = 500 hm3 and (1-ps) = 75%, P(STST*) 0.25
•P(RLj) prj - Reservoir Level Constraint
For Restriction Level 1, P(RL1) < 0.25; pr1 – Restriction level 1 prob.
Similarly for level 2, P(RL2) < 0.10; pr2 – Restriction level 2 prob.
Reservoir Simulation (for each ensemble ‘k’)
• Inflow Forecast : qtk; t=1…,T; k=1,…,N
• Continuity Equation: t=1,2, …, T
• SDt = -St | St < 0 (Account the Deficit)
• Rti=btiRi (Target Release for each user)
• Evaporation :
n
i
titttt REqSS1
1
2)2/)(( 11 tttt SSE
Presentation Outline
• Forecast Producers and Consumers
– Perspectives on Risk: Supply and Demand
• Dynamic Risk Management Framework
• Insights from Retrospective Analyses
– Ceara, North East Brazil
– Angat, Philippines
– Falls Lake, North Carolina
• Opportunities and Challenges
TALE OF TWO RIVER BASINS Jaguaribe-Metropoilitan
HydroSystem, Ceara, Brazil
Angat Reservoir, Philippines
Angat Reservoir during the 1997-98 El Nino
Hydroclimatology of the Basins JMH, Ceara, NE Brazil
• Semi-Arid
• One Rainy season,
Rest Zero flows
Angat, Philippines
• Humid
• Two Rainy Seasons
(Jun-Sep) & (Oct-Dec) Seasonality of Oros Inflow
0
50
100
150
200
250
300
350
400
1 2 3 4 5 6 7 8 9 10 11 12
Month
Flo
w (
m^
3/s
)
Mean
Median
Quantile (75)
Quantile (25)
Quantile (90)
Quantile (10)
Seasonality of rain determined by N-S migration of the ITCZ
0
50
100
150
200
250
300
350
JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC
Month
Str
eam
flo
w (
in h
m3)
0
50
100
150
200
250
300
350
400
450
500
Rain
fall (
mm
)
Streamflow
Rainfall
JJAS – 30%
OND – 46%
3-months lag correlation
(Nino3.4,QJJAS) = -0.20
(Nino3.4,QOND) = -0.51
Predictors Correlation
Nino 3.4
Dipole
-0.31
-0.42
Water Management Context JMH, Ceara, NE Brazil
Angat, Philippines
Agriculture
Julyt Julyt+1 Jant+1 Dect+1
Seasonal Variation Rain/Flow
Municipal and Industrial
Priority Uses
• Municipal
• Industrial
• Agriculture
ANGAT H.E. PLANT
150
160
170
180
190
200
210
220
JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC
EL
EV
AT
ION
(m
)
1996 1997 1998 1999 2000 2001 UPPER LOWER
Priority Uses
• Municipal
• Industrial
• Agriculture
• Hydropower
Storage/Annual
Demand Ratio: 0.72
Storage/Annual
Demand Ratio: 5.1
Hydroclimatology of the Basins JMH, Ceara, NE Brazil Angat, Philippines
• ECHAM4.5 Precipitation
Forecasts Forced with
Persisted SST conditions
Seasonality of rain determined by N-S migration of the ITCZ
Predictors Correlation
Nino 3.4
Dipole
-0.31
-0.42
(PF,Qobs):0.51
ONDJF
Climate Information based Streamflow Forecasts JMH, Ceara, NE Brazil
• Predictors: Nino3.4 & Atlantic Dipole
• Semi-parametric Resampling algorithm
Angat, Philippines
• ECHAM 4.5 ONDJF Forecasts with persisted SSTs
• Parametric Regression
0
50
100
150
200
250
300
350
400
1968 1978 1988 1998
Year
Str
eam
flo
w (
MC
M)
ONDJF-obs
ONDJF-pred
(Qpred,Qobs):0.58
0
25
50
75
100
125
150
175
200
225
1970 1975 1980 1985 1990 1995
Year
Flo
w (
m3/s
)
obsFirst QuartileMedianThird QuartileMax
(Qobs,Qpred) = 0.75
De Souza et al., 2003
Sankarasubramanian et al., 2008
Retrospective Analyses on Water Allocation
JMH, Ceara, NE Brazil:1990 – 2000;Annual Demand
-20
0
20
40
60
80
100
120
1991 1992 1993 1994 1995 1996 1997 1998 1999 2000
Year
Fo
recas
t -
Zero
In
flo
w Y
ield
(h
m3)
0
10
20
30
40
50
60
70
Ob
se
rve
d F
low
s (
m3/s
)
Agriculture
Industrial
Flow
Forecast
Sankarasubramanian et al., WRR, 2009.
Oros - System Losses
-100
-90
-80
-70
-60
-50
-40
-30
-20
-10
0
10
1991 1992 1993 1994 1995 1996 1997 1998 1999 2000
Year
Fo
reca
st
- Z
ero
(in
hm
3)
0
10
20
30
40
50
60
70
Ob
se
rve
d F
low
s (
in m
3/s
)
Evaporation+spill
Storage in July
Observed Flows
Angat, Philippines
The Angat Reservoir during the 1997-98 El Nino (September 12,
1998 – RWL = 158.15 m AMSL)
ANGAT H.E. PLANT
150
160
170
180
190
200
210
220
JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC
EL
EV
AT
ION
(m
)
1996 1997 1998 1999 2000 2001 UPPER LOWER
IRI Forecast for OND 1998
Retrospective Analyses on Water Allocation Angat, Philippines: 1987-2001 ONDJF Allocation
0
100
200
300
400
500
600
1987 1989 1991 1993 1995 1997 1999 2001
Year
Oco
tber
All
ocati
on
(h
m3)
0
50
100
150
200
250
300
350
400
Ob
se
rve
d I
nfl
ow
(h
m3
)
Municipal
Irrigation
hydropower
M&I target
Irrigation target
Observed Flow
Performance - updated Forecasts
0
0.1
0.2
0.3
0.4
0.5
0.6
Target Month
Co
rre
lati
on
OctoberNovemberDecemberJanuaryFebruary
Oct Nov Dec Jan Feb
Sankarasubramanian et al., 2008, J.hydromet
Angat- Spill Volume (Max Hydro)
0
50
100
150
200
250
300
350
400
450
1987 1989 1991 1993 1995 1997 1999 2001
Years
Sp
ill
Vo
lum
e (
in h
m3
)
0
50
100
150
200
250
300
350
400
Ob
se
rve
d In
flow
ActualUpdated ForecastOctober ForecastObserved Inflow
Sankarasubramanian et al., 2009, JAMC
Retrospective Analyses on Water Allocation
Angat, Philippines: 1987-2001 ONDJF Allocation
0
200
400
600
800
1000
1200
1400
1987 1989 1991 1993 1995 1997 1999 2001
Year
Hyd
rop
ow
er
Ge
ne
rate
d (
in G
WH
)
0
50
100
150
200
250
300
350
400
Ob
se
rve
d In
flow
ActualUpdated ForecastOctober ForecastObserved
Sankarasubramanian et al., 2009, JAMC
Meeting February Target Storage
0
100
200
300
400
500
600
700
800
Oct Nov Dec Jan FebForecast Issued
Fe
bru
ary
Sto
rag
e (
hm
3)
198919911997Target Storage
Sankarasubramanian et al., 2009, JAMC
Utility of Forecasts in improving
hydropower generation
Maurer and Lettenmaier, 2004, Jclim.
Utility of Forecasts as storage/inflow
Maurer and Lettenmaier, 2004, Jclim.
Utility of Forecasts As Storage/Demand
0
1
10
0.0 1.0 2.0 3.0 4.0 5.0 6.0
Storage/Demand
% Im
pro
vem
en
t
Correlation = 1.0
Correlation = 0.75
Correlation = 0.5
Angat Oros
Sankarasubramanian et al., WRR, 2009.
Insights from Retrospective Analyses
• For seasonal forecasts to be useful
– Initial storage should constrain the allocation
– If not, 100% reliability; Most systems belong to this
category, since reservoirs are designed to reduce
the variability and ensure reliability of supply.
• Use end of season target storage constraint
– If initial storage does not constrain allocation
– If skill is good only during a particular season
– To enforce restrictions for below normal conditions
– To reduce spillage and increase allocation
(primarily hydropower) for above normal conditions
• Perspectives from Forecasting
– Update the forecasts within the season (very
beneficial for hydropower systems)
– Multimodel climate forecasts are better, since it
reduces aggressiveness of individual models
• Forecasts are more useful than climatology
– Within year storage systems (typically humid
basins) than over year (arid basins) systems
– Reducing system losses (spill and evaporation)
– Systems with low storage/annual demand ratio
– Multiple uses constraining the allocation process
Insights from Retrospective Analyses
Opportunities and Challenges
• Seasonal Climate Forecasts Applications
for Water Management
– Multimodel Combination
• Well calibrated forecasts improves confidence
– Nutrient Loadings Forecasts
• Scope for Extending this framework for Nutrient
Allocation
– Water and Energy Systems Management
• Covariability between precipitation and temperature
Why multimodel combination reduces uncertainty?
Weigel et al., QJRMS, 2008.
Mu
ltim
od
el c
om
bin
ati
on
-U
nc
ert
ain
ty R
ed
uc
tio
n
Mu
ltim
od
el c
om
bin
ati
on
-U
nc
ert
ain
ty R
ed
uc
tio
n
Select categorical climate forecasts/predictions, ,
m
i tQ , where m=1,2...,M
(M=8) denotes the model index including climatology, with i=1, 2..., N (N=3) representing
the categories in year ‘t’ with t=1,2…, T (T= 46 years).
Obtain the squared error, SEtm, between the ensemble mean and the observed
precipitation/temperature for each year for all GCMs.
Based on DJF Nino3.4 (X) as the predictor, compute the distance between the current
Nino3.4, Xt, and the rest of the Nino3.4, Xl, where l=1,2..., T-1 (leaving ‘t’ year out).
Choose the number of neighbors, K, and compute Mean Square Error (MSE) over ‘K’
neighbors using: ( )
1
1 Km m
t, K j
j
SEK
Compute weights ( ,
m
t Kw ) for each model for each time step based on MSE over ‘K’
neighbors
M
m
m
Kt
m
Ktm
Ktw
1
,
,
,
/1
/1
Obtain categorical forecasts/predictions of multimodels, ,
MM
i tQ , based on individual models’
weights ( ,
m
t Kw ): , ,
1, ,
,
1
Mm m
t K i tMM mi t K M
m
t K
m
w Q
Q
w
Get the skill of the multimodel forecasts/predictions, , ,,MM MM
t K t KSE RPS (Rank Probability Score)
(Devineni et al., WRR, 2008)
Reliability of Multimodel Forecasts – BN Precipitation
(Devineni and Sankarasubramanian, Monthly Weather Review, 2010)
Why conditioned multimodel better?
(Devineni and Sankarasubramanian, Monthly Weather Review, 2010)
0
10
20
30
40
50
60
0.0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1991 1993 1995 1997 1999 2001 2003 2005
Ob
serv
ed
Str
eam
flo
w (
cm
s)
Pro
b(S
T<
ST
* )
Year
Regression
Resampling
Multimodel
Climatology
Observed
0.33 percentile
0.66 percentile
Probability of Meeting the Target Storage
Golembesky et al., 2008
Invoking Restriction based on Target Storage Probabilities
0
20
40
60
80
100
120
140
0
10
20
30
40
50
60
70
80
1991 1992 1993 1994 1997 1998 2002 2005
Ob
serv
ed
S
tream
flo
w,
cfs
Restr
icti
on
(%
)
Year
Resampling
Multimodel
Regression
Observed
(a)
0
20
40
60
80
100
120
140
0
2000
4000
6000
8000
10000
12000
1991 1992 1993 1994 1997 1998 2002 2005
Ob
serv
ed
S
tream
flo
w,
cfs
Dif
fere
nce i
n S
ep
tem
ber
Sto
rag
e, acre
-feet
Year
Resampling
Multimodel
Regression
Observed
(b)
Golembesky et al., 2008
Water Quality Management
• Water Quality Trading
– Successful programs in Neuse and Tar basins
– Association - Municipal and Industrial discharges
– Target nutrient loadings – Point and nonpoint
– Trading – Point to point and point to nonpoint
– Point to nonpoint – Cost share program for BMP
• Opportunity to use Forecasts
– Pre-season estimates of loadings from runoff
– Optimal loadings between point and nonpoint
– Forecasts work better with contracts/trading
Initial Results on Nutrient Forecasts
Covariability in precipitation and temperature
• Positive (Negative) Correlation during winter
– Tennessee Valley, New England (Upper Mid West)
• Negative Correlation during summer
– Midwest, Midwest and part Southeast
Winter Summer
Opportunities and Challenges
• Seasonal to Interannual Climate Forecasts
– Uncertainty Reduction and Reliable Forecasts
– Appropriate Policy Instruments – e.g., water
contracts with specified reliability, penalties and
tariffs.
– Climate Information based River Basin
Management
• Seasonal Nutrients Allocation and Water Quality Trading
• Combined Water and Energy Systems Management
Acknowledgements
• IRI, Columbia University, Palisades
– Upmanu Lall, Naresh Devineni
• FUNCEME, Ceara, North East Brazil
– Assis Filho De Souza
• PAGASA, Manila, Philippines
– Susan Espinueva
• NC State University
– Kurt Golembesky, Jeseung Oh
Related Publications • Sankarasubramanian, A., U.Lall, F.D.Souza Filho, A.Sharma (2009), Improved
Water Allocation utilizing Probabilistic Climate Forecasts: Short-term Water
Contracts in a Risk Management Framework, Water Resources Research.
• Sankarasubramanian, A., U. Lall, and S. Espunevea (2009), Utility of
Operational Streamflow Forecasts in Improving within-season Reservoir
Operation, Journal of Applied Climatology & Meteorology.
• Golembesky, K., and A. Sankarasubramanian, and N. Devineni (2009), Improved
Management of Falls Lake Reservoir during the Summer Season using Climate
Information based Monthly Streamflow Forecasts: Role of Restrictions in
Water supply and Water Quality Management, Journal of Water Resources
Planning and Management, 2009.
• Devineni, N., A. Sankarasubramanian, and S. Ghosh (2008), Multi-model
Ensembling of Probabilistic Streamflow Forecasts: Role of Predictor State
Space in Skill Evaluation, Water Resources Research, 44, W09404,
doi:10.1029/2006WR005855.
• Sankarasubramanian, A., U. Lall, and S. Espuneva (2008), Role of
Retrospective Forecasts of GCMs Forced with Persisted SST anomalies in
Operational Streamflow Forecasts Development, Journal of Hydrometeorology,
9(2), 212-227.