the great lakes runoff intercomparison project · lauren fry1,2, andrew d. gronewold2, vincent...

1
0 3 04046000 0 150 04056500 0 111 04059000 0 359 04067500 0 92 04069500 0 71 04071765 0 554 04084445 0 15 04085200 0 68 04085427 0 115 04086600 0 31 04087240 0 25 04093000 0 10 04096015 0 47 04102500 0 220 04108660 0 203 04121970 0 57 04122500 0 8 04126740 0 9 04126970 Oct 1999 Oct 2001 Oct 2003 Oct 2005 Oct 2007 Oct 2009 0 8 04127800 AFINCH LBRM CHPS ARM2 (using basin AR when no observation is available within subbasin) ARM1 (no simulated discharge when no observation is available within subbasin) The Great Lakes Runoff Intercomparison Project Lauren Fry 1,2 , Andrew D. Gronewold 2 , Vincent Fortin 3 , David Holtschlag 4 , Steven Buan 5 , Anne Clites 2 , Timothy Hunter 2 , Frank Seglenieks 6 , Erika Klyszejko 7 , Carol Luukkonen 4 , Laura Diamond 5 , and Kandace Kea 8 1 Cooperative Institute for Limnology and Ecosystems Research, University of Michigan, Ann Arbor, MI, USA ([email protected]), 2 NOAA, Great Lakes Environmental Research Laboratory, Ann Arbor , MI, USA; 3 Environmental Numerical Prediction Section, Environment Canada, Dorval, QC, Canada 4 U.S. Geological Survey Michigan Water Science Center, Lansing, MI, USA; 5 NOAA, National Weather Service, North Central River Forecast Center, Chanhassen, MN, USA 6 Boundary Water Issues, Environment Canada, Burlington, ON, Canada; 7 Water Survey of Canada, Environment Canada, Ottawa, ON, Canada; 8 Howard University, Washington, DC, USA N A T I O N A L O C E A N I C A N D A T M O S P H E R I C A D M I N I S T R A T I O N U . S . D E P A R T M E N T O F C O M M E R C E Cooperative Institute for Limnology and Ecosystems Research CILER Abstract No. H51I-1463 Introduction As a continuation of investments in the development of alternative methods for estimating major components of the Great Lakes water budget through the recently- completed International Joint Commission (IJC) International Upper Great Lakes Study (IUGLS), representatives from Environment Canada (EC), U.S. Geological Survey (USGS), NOAA’s National Weather Service (NWS), and NOAA’s Great Lakes Environmental Research Laboratory (GLERL) have formed a bi-national collaboration to assess alternative methods for simulating runoff across large lake basins. Models or modeling frameworks (and contributing agencies) participating in the project include (but are not limited to) Analysis of Flows in Networks of Channels (or AFINCH, from USGS), the Community Hydrologic Prediction System (or CHPS, from NWS), several configurations of the Modélisation Environmentale Communautaire - Surface Hydrology system (or MESH, from Environment Canada), the Large Basin Runoff Model (or LBRM, from GLERL) as well as the Area Ratio Method of extrapolation (or ARM, from GLERL). Initial research considers the Lake Michigan Basin (GRIP-M); a next phase will consider Lake Ontario (GRIP-O). Models The GRIP analysis considers eight models and model configurations that represent a variety of types of runoff models and operate at different spatial and temporal scales (Figure 1 and Table 1). Table 1. Summary of models evaluated in the GRIP-M project. Regression Lumped Conceptual Distributed Conceptual Coupled Uncoupled Temporal Resolution ARM X X Daily, aggregated to monthly AFINCH X X Monthly LBRM X X X Monthly CHPS X X Sub-daily, aggregated to monthly MESH-Standalone X X Daily or Monthly MEC-MESH X X Daily or Monthly MESH-HydroSHEDS with high-resolution routing X X Daily or Monthly MESH-HydroSHEDS with land surface and routing X X Daily or Monthly 04067500 04059000 04056500 04046000 04071765 04069500 04127800 04121970 04122500 04126970 04126740 04085427 04086600 04084445 04085200 04108660 04087240 04102500 04096015 04093000 Validation Gages Model Descriptions ARM The GLERL ARM is a two-step process operating on 121 subbasins in the Great Lakes basin, 27 of which comprise the Lake Michigan basin (Figure 1b) (Croley II & Hartmann 1986; Croley II & He 2002). The first step applies the ARM in partially gaged subbasins (on each day), and the second step is to extrapolate from these partially gaged subbasins to totally ungaged basins by applying ARM a second time. Time series of subbasin monthly runoff estimates are available online, and span the period of 1898-2010 (http://www.glerl.noaa.gov/). Additionally, ARM simulations provided the synthetic subbasin runoff time series that constrained calibration of the Large Basin Runoff Model. AFINCH AFINCH (described by Holtschlag 2009) was developed by USGS to estimate streamflows and water yields throughout large regions as part of the Great Lakes Basin Pilot Project of the National Water Availability and Use Program. The model simulates monthly flow in each NHDplus flowline (Figure 1c) using step-wise linear regression models relating monthly water yield observations to geospatial climate and land-cover data. The model is configured to incorporate water-use data, and can be constrained to observations at gaged flowlines. LBRM LBRM (Croley II & He 2002) is a lumped parameter conceptual model that simulates water transport through cascading tanks, and provides forecasts of runoff to the Great Lakes Advanced Hydrologic Prediction System (described by Gronewold et al. 2011). The model, which has nine calibrated parameters, remains the only conceptual rainfall- runoff model to be systematically applied to 121 subbasins in the Great Lakes (Figure 1b) (Coon et al. 2011). The nine parameters were calibrated by conditioning the LBRM on a synthetic discharge time series provided by GLERL’s ARM simulations. CHPS CHPS is a modeling and operational infrastructure designed to be integrated into the NWS Advanced Weather Interactive Processing System (AWIPS), and provides the basis for sharing new and existing models with the broader hydrologic community (Roe et al. 2010). Data import, storage, and display are provided by the Delft Flood Early Warning System (FEWS), and hydrologic and hydraulic models are provided by the NWS and U.S. Army Corps of Engineers (USACE). For the GRIP analysis, CHPS was implemented using the Sacramento Soil Moisture Accounting Model, operating on the hydrologic units in Figure 1d. Model parameters are estimated by calibration using regression models at gaged hydrologic units and by assignment at ungaged units, based on landscape characteristics and proximity. Four Configurations of MESH Environment Canada uses its Modélisation Environmentale Communautaire - Surface Hydrology (MESH) model (Pietroniro et al. 2007), a distributed model combining land surface models with land surface parameterization and hydrologic routing, to forecast runoff to the lakes from both the U.S. and Canadian portions of the basin. The GRIP project will consider four configurations of MESH (Table 2). Table 2. MESH Configurations. Configuration Coupled Atmospheric Forcing resolution Land Surface Model Routing Model Response Unit Approach MESH-Standalone 10 arcsec CLASS (10 arcmin) 1 WATROUTE (10 arcmin) 3 Figure 1e Grouped MEC-MESH X 10 arcsec ISBA (10 arcmin) 2 WATROUTE (10 arcmin) 3 Figure 1e Single MESH- HydroSHEDS with high-resolution routing X 10 arcsec ISBA (10 arcmin) 2 Based on HydroSHEDS (15 arcsec) 4 Figure 1f Single MESH- HydroSHEDS with land surface and routing X 3 arcsec ISBA (15 arcsec) 2 Based on HydroSHEDS (15 arcsec) 4 Figure 1f Single 1 Canadian Land Surface Scheme (CLASS) ( Verseghy 2000) 2 Interactions between Surface– Biosphere–Atmosphere (ISBA) (Bélair et al. 2003) 3 Kouwen (2010) 4 Lehner et al. (2006) Figure 1. (a) Locations of the USGS gages used for the validation component of the project. (b-f) Spatial framework of each model considered in the GRIP-M analysis. (b) LBRM and ARM are lumped parameter and regional regression models, respectively, operating on 27 subbasins in the basin. (c) AFINCH applies a regression model to 31,820 NHDplus flowlines in the basin, constraining flow to observed discharge where gages provide monthly observations. (d) CHPS is a lumped parameter model operating on 211 hydrologic units in the basin. (e-f) MESH is a distributed model configured for (e) a low resolution land surface model (MESH-Standalone and MEC-MESH) or (f) high resolution routing or high resolution routing and land surface models (2 configurations of MESH-HydroSHEDS). Methods The GRIP-M project involves side-by-side comparison of the time series of runoff to Lake Michigan, cumulative runoff to Lake Michigan for a common simulation period, and model skill at 20 validation gages in the basin. Because the analysis takes place within the context of large scale water balance modeling, we selected the 20 validation gages near the coast. These 20 gages are removed from any calibration or simulation procedures during a common validation period (2002-2010), and simulated monthly discharge time series are compared with the observed flow at these gages. For ARM, we consider two alternative simulation methods: (1) using only the area ratio estimated for the subbasin, leaving gaps in the series when no observation is available within the subbasin, and (2) during months for which no observation is recorded, the area ratio of the lake basin is applied to estimate flow at the gage, essentially the second step of the GLERL implementation of ARM. Preliminary Results Preliminary simulations of Lake Michigan inflow are available for ARM, LBRM, AFINCH, MESH- Standalone, and CHPS. Each model simulates similar peak and low flows (Figure 2). However, CHPS and LBRM typically simulate higher flows and MESH-Standalone flows are lower. ARM and AFINCH, which both incorporate gage information, both simulate flows in the middle of the range of model simulations. Although time series simulations may appear similar among the models, differences over time would result in accumulated error in water level simulations drawing on runoff from these models (Figure 3). Preliminary validation results for CHPS, ARM, AFINCH, and LBRM suggest varying model skill (Figure 4, Figure 5, and Table 3). In general, CHPS and LBRM somewhat over-predict discharge, consistent with their positions on the plot of cumulative runoff (Figure 3). The prediction skill of ARM and AFINCH varies, with generally improved model skill when other gage observations are available within the subbasin. There does not appear to be a systematic under- or over-prediction bias associated with ARM or AFINCH simulations; however absolute bias can be large, especially from simulations produced by ARM2, which uses the basin area ratio when no observation is available within a subbasin. Table 3. Goodness-of-fit statistics for simulations at the 20 validation gages, following recommendations by Moriasi et al. (2007) and computed with R package HydroGOF (Zambrano-Bigiarini 2011). NSE is the Nash Sutcliffe Efficiency, Percent Bias is the average percent bias (with positive values indicating overestimation), and RSR is the RMSE-observations standard deviation ratio. NSE PBIAS RSR Gage ARM1 ARM2 CHPS AFINCH LBRM ARM1 ARM2 CHPS AFINCH LBRM ARM1 ARM2 CHPS AFINCH LBRM 04046000* NA 0.32 NA 0.67 0.16 NA 11.10 NA 32.4 64.9 NA 0.82 NA 0.57 0.91 04056500* NA 0.24 0.85 0.73 0.63 NA -24.00 -9.90 -19.5 19.5 NA 0.87 0.38 0.51 0.61 04059000 0.92 0.92 0.75 0.85 0.71 4.50 4.50 8.30 19.5 23.6 0.28 0.28 0.50 0.38 0.54 04067500 1.00 1.00 0.25 0.64 0.67 1.30 1.30 35.10 13.9 21 0.06 0.06 0.86 0.59 0.57 04069500 0.99 0.99 0.51 0.99 0.52 2.20 2.20 36.20 2.7 27.2 0.08 0.08 0.70 0.09 0.69 04071765 0.94 0.94 0.64 0.95 0.54 5.80 5.80 26.40 5.1 27.2 0.24 0.24 0.59 0.22 0.67 04084445* -0.44 -0.18 0.57 0.92 0.67 -38.00 14.70 22.60 1.2 2.4 1.18 1.08 0.65 0.29 0.57 04085200* NA 0.19 0.66 0.73 0.48 NA 72.20 18.00 12.9 8.8 NA 0.90 0.58 0.52 0.72 04085427 0.47 0.47 0.65 0.74 0.5 43.90 43.90 28.50 16.2 2.2 0.72 0.72 0.59 0.5 0.7 04086600 0.01 0.01 0.56 0.93 0.73 43.80 43.80 13.40 2.2 6.8 0.99 0.99 0.66 0.26 0.51 04087240 0.71 0.71 0.79 0.93 0.17 26.80 26.80 3.60 -2.3 15.9 0.54 0.54 0.46 0.27 0.91 04093000 0.49 0.49 0.71 0.4 0.7 5.30 5.30 -15.90 -14.5 -3.7 0.71 0.71 0.53 0.77 0.55 04096015 0.53 0.53 0.73 0.64 0.72 12.70 12.70 20.30 -2 3 0.68 0.68 0.52 0.6 0.53 04102500 0.67 0.67 0.66 0.64 0.64 -8.50 -8.50 5.70 -12 -3.1 0.57 0.57 0.58 0.6 0.6 04108660 0.88 0.88 0.88 0.84 0.61 -2.10 -2.10 1.10 -9.9 -8.7 0.35 0.35 0.34 0.39 0.62 04121970 0.84 0.84 0.54 0.96 0.75 8.80 8.80 19.60 2.2 11.9 0.39 0.39 0.68 0.19 0.5 04122500 0.88 0.88 0.72 0.57 0.78 -4.00 -4.00 9.40 3.9 0.2 0.34 0.34 0.53 0.66 0.46 04126740* NA -11.11 -1.61 -10.06 -18.47 NA -4.70 -11.70 18.8 44.2 NA 3.47 1.61 3.31 4.4 04126970* NA -1.34 -0.97 0.06 -5.59 NA 11.70 33.80 2.2 62 NA 1.52 1.40 0.96 2.56 04127800* NA -54.68 -0.20 -9.92 -31.14 NA -65.90 6.90 -26.6 -50.6 NA 7.43 1.09 3.29 5.65 * Gages in ARM subbasins for which there is no observation during some period. Validation Gages CHPS ARM and LBRM Validation Gages Validation Gages Conclusions Preliminary results indicate that all models under consideration for the GRIP-M project simulate similar timing of peak and low flows. However, plots of cumulative runoff suggest that biases among the models result in different simulated accumulated depth of runoff to Lake Michigan over time, and preliminary validation at 20 gages suggest varying model skill. Each model was developed for a different purpose (e.g. large scale water balance simulation and forecasting, investigation of impacts of land use and water withdrawals on stream flow, and flood forecasting), and the GRIP-M project is the first to compare these models for use in regional water balance simulation. Future GRIP work will involve investigating the sources of model error and the potential for each model to improve large scale water balance simulations. Figure 4. Time series of simulated runoff (cms) at the 20 validation gages. Gage locations are shown in Figure 1a. Figure 5. Spatial representation of the goodness-of-fit statistics for simulations at the 20 validation gages. (a) ARM1 with no simulations when no observations available within the subbasin, (b) ARM2 with simulation provided by basin-wide area ratio when no observations available within the subbasin, (c) CHPS, (d) AFINCH, and (e) LBRM. Gages for which no simulation is provided by a model are shown as black points. Acknowledgements This work was partially completed under a post-doctoral fellowship with the Cooperative Institute for Limnology and Ecosystems Research, awarded under a Cooperative Agreement between the University of Michigan and the NOAA Great Lakes Environmental Research Laboratory. Additional support was provided by NOAA’s Educational Partnership Program. References Anderson, E.J., Schwab, D.J. & Lang, G.A., 2010. Real-time hydraulic and hydrodynamic model of the St. Clair River, Lake St. Clair, Detroit River system. Journal of Hydraulic Engineering, 136(8), pp.507–518. Bélair, S. et al., 2003. Operational Implementation of the ISBA Land Surface Scheme in the Canadian Regional Weather Forecast Model . Part II : Cold Season Results. Journal of Hydrometeorology, 4(2), pp.371–386. Coon, W.F. et al., 2011. Compilation of watershed models for tributaries to the Great Lakes, United States, as of 2010, and identification of watersheds for future modeling for the Great Lakes Restoration Initiative: U.S. Geological Survey Open-File Report 2011-1202, Reston, VA: U.S. Department of the Interior, U.S. Geological Survey. Available at: http://pubs.usgs.gov/of/2011/1202. Croley II, T.E. & Hartmann, H.C., 1986. NOAA Technical Memorandum ERL GLERL-61: Near-Real-Time Forecasting of Large-Lake Water Supplies; A User’s Manual, Ann Arbor, MI. Croley II, T.E. & He, C., 2002. Great Lakes Large Basin Runoff Modeling. In Second Federal Interagency Hydrologic Modeling Conference, Subcommittee on Hydrology of the Interagency Advisory Committee on Water Data. Las Vegas, NV. Gronewold, A.D. et al., 2011. An appraisal of the Great Lakes advanced hydrologic prediction system. Journal of Great Lakes Research, 37(3), pp.577–583. Available at: http://linkinghub.elsevier.com/retrieve/pii/ S0380133011001638 [Accessed March 20, 2012]. Holtschlag, D.J., 2009. Scientific Investigations Report 2009-5188: Application Guide for AFINCH (Analysis of Flows in Networks of Channels) Described by NHDPlus, Scientific Investigations Report 2009–5188, Reston, VA. Available at: http://pubs.usgs.gov/sir/2009/5188/ [Accessed May 24, 2012]. Kouwen, Nicholas, 2010. WATFLOOD/WATROUTE Hydrological Model Routing & Flow Forecasting System, Waterloo, ON: Department of Civil Engineering, University of Waterloo. Lehner, B., Verdin, K. & Jarvis, A., 2006. HydroSHEDS Technical Documentation Version 1.0. Moriasi, D.N. et al., 2007. Model evaluation guidelines for systematic quantification of accuracy in watershed simulations. Transactions of the American Society of Agricultural and Biological Engineers, 50(3), pp.885–900. Pietroniro, A. et al., 2007. Development of the MESH modelling system for hydrological ensemble forecasting of the Laurentian Great Lakes at the regional scale. Hydrology and Earth System Sciences, 11(4), pp.1279–1294. Available at: http://www.hydrol-earth-syst-sci.net/11/1279/2007/. Roe, J. et al., 2010. Paper 7B.3: Introduction of NOAA’s Community Hydrologic Prediction System. In 26th Conference on Interactive Information and Processing Systems (IIPS) for Meteorology, Oceanography, and Hydrology. Atlanta, GA. Verseghy, D.L., 2000. The Canadian land surface scheme (CLASS): Its history and future. Atmosphere-Ocean, 31(1), pp.1–13. Zambrano-Bigiarini, M., 2011. hydroGOF: Goodness-of-fit functions for comparison of simulated and observed hydrological time series. R package version 0.3-2. Available at: http://cran.r-project.org/package=hydroGOF . a b c d e f Neg PBIAS ARM1 -38 - -24 -23 - -9 -8 - -4 -3 - 0 Pos PBIAS ARM1 1 - 2 3 - 6 7 - 13 14 - 27 28 - 44 RSR ARM1 0.06 - 0.30 0.31 - 0.50 0.51 - 0.70 0.71 - 1.00 1.01 - 1.18 NSE ARM1 -0.44 - 0.00 0.01 - 0.50 0.51 - 0.70 0.71 - 0.90 0.91 - 1.00 Neg PBIAS ARM2 -66 - 50 51 - -24 -23 - -9 -8 - -4 -3 - 0 Pos PBIAS ARM2 1 - 2 3 - 9 10 - 15 16 - 27 28 - 72 RSR ARM2 0.06 - 0.30 0.31 - 0.50 0.51 - 0.70 0.71 - 1.00 1.01 - 7.43 NSE ARM2 -54.68 - 0.00 0.01 - 0.50 0.51 - 0.70 0.71 - 0.90 0.91 - 1.00 a b Neg PBIAS CHPS -16 - -9 Pos PBIAS CHPS 1 - 2 3 - 9 10 - 15 16 - 27 28 - 37 RSR CHPS 0.34 - 0.50 0.51 - 0.70 0.71 - 1.00 1.01 - 1.61 NSE CHPS -1.61 - 0.00 0.01 - 0.50 0.51 - 0.70 0.71 - 0.90 0.91 - 1.00 c Neg PBIAS AFINCH -27 - -24 -23 - -9 -8 - -4 -3 - 0 Pos PBIAS AFINCH 1 - 2 3 - 6 7 - 13 14 - 27 28 - 32 RSR AFINCH 0.09 - 0.30 0.31 - 0.50 0.51 - 0.70 0.71 - 1.00 1.01 - 3.31 NSE AFINCH -10.06 - 0.00 0.01 - 0.50 0.51 - 0.70 0.71 - 0.90 0.91 - 1.00 Pos PBIAS LBRM -51 - -24 -23 - -9 -8 - -4 -3 - 0 Neg PBIAS LBRM 0 - 2 3 - 6 7 - 13 14 - 27 28 - 65 RSR LBRM 0.46 - 0.50 0.51 - 0.70 0.71 - 1.00 1.01 - 5.65 NSE LBRM -31.14 - 0.00 0.01 - 0.50 0.51 - 0.70 0.71 - 0.78 d e Environment Canada Environnement Canada Great Lakes Environmental Research Laboratory GLERL W E A T H E R N A T I O N A L S E R V I C E ARM LBRM MESH Standalone CHPS AFINCH 1000 2000 3000 1940s 1000 2000 3000 1950s 1000 2000 3000 1960s 1000 2000 3000 1970s 1000 2000 3000 1980s 1000 2000 3000 1990s ..0 ..1 ..2 ..3 ..4 ..5 ..6 ..7 ..8 ..9 ..0 1000 2000 3000 2000s Discharge (cms) Figure 2. Preliminary time series of simulated runoff. Figure 3. Cumulative runoff to Lake Michigan for the common simulation period (2004-2010) in units of depth over the lake. 2005 2006 2007 2008 2009 2010 0 1 2 3 4 month depth (m) ARM LBRM MESH Standalone CHPS AFINCH

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Page 1: The Great Lakes Runoff Intercomparison Project · Lauren Fry1,2, Andrew D. Gronewold2, Vincent Fortin 3, David Holtschlag4, Steven Buan5, Anne Clites 2, Timothy Hunter 2, Frank Seglenieks6,

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AFINCH

LBRM

CHPS

ARM2 (using basin AR when no observation is available within subbasin)

ARM1 (no simulated discharge when no observation is available within subbasin)

The Great Lakes Runoff Intercomparison ProjectLauren Fry1,2, Andrew D. Gronewold2, Vincent Fortin3, David Holtschlag4, Steven Buan5, Anne Clites2, Timothy Hunter2,

Frank Seglenieks6, Erika Klyszejko7, Carol Luukkonen4, Laura Diamond5, and Kandace Kea8

1Cooperative Institute for Limnology and Ecosystems Research, University of Michigan, Ann Arbor, MI, USA ([email protected]), 2NOAA, Great Lakes Environmental Research Laboratory, Ann Arbor , MI, USA; 3Environmental Numerical Prediction Section, Environment Canada, Dorval, QC, Canada

4U.S. Geological Survey Michigan Water Science Center, Lansing, MI, USA; 5NOAA, National Weather Service, North Central River Forecast Center, Chanhassen, MN, USA6Boundary Water Issues, Environment Canada, Burlington, ON, Canada; 7Water Survey of Canada, Environment Canada, Ottawa, ON, Canada; 8Howard University, Washington, DC, USA

NATI

ON

AL O

CEANIC AND ATMOSPHERIC ADM

INISTRATIO

N

U.S.DEPARTMENT OF COMMERCE

Cooperative Institute for Limnologyand Ecosystems Research

CILER

Abstract No. H51I-1463

IntroductionAs a continuation of investments in the development of alternative methods for estimating major components of the Great Lakes water budget through the recently-completed International Joint Commission (IJC) International Upper Great Lakes Study (IUGLS), representatives from Environment Canada (EC), U.S. Geological Survey (USGS), NOAA’s National Weather Service (NWS), and NOAA’s Great Lakes Environmental Research Laboratory (GLERL) have formed a bi-national collaboration to assess alternative methods for simulating runoff across large lake basins. Models or modeling frameworks (and contributing agencies) participating in the project include (but are not limited to) Analysis of Flows in Networks of Channels (or AFINCH, from USGS), the Community Hydrologic Prediction System (or CHPS, from NWS), several configurations of the Modélisation Environmentale Communautaire - Surface Hydrology system (or MESH, from Environment Canada), the Large Basin Runoff Model (or LBRM, from GLERL) as well as the Area Ratio Method of extrapolation (or ARM, from GLERL). Initial research considers the Lake Michigan Basin (GRIP-M); a next phase will consider Lake Ontario (GRIP-O).

ModelsThe GRIP analysis considers eight models and model configurations that represent a variety of types of runoff models and operate at different spatial and temporal scales (Figure 1 and Table 1).

Table 1. Summary of models evaluated in the GRIP-M project.

R

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ssio

n

Lum

ped

Con

cept

ual

D

istri

bute

d C

once

ptua

l

Cou

pled

U

ncou

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Temporal Resolution

ARM X X Daily, aggregated to monthly

AFINCH X X Monthly

LBRM X X X Monthly

CHPS X X Sub-daily, aggregated to monthly

MESH-Standalone X X Daily or Monthly

MEC-MESH X X Daily or Monthly

MESH-HydroSHEDS with high-resolution routing X X Daily or Monthly

MESH-HydroSHEDS with land surface and routing X X Daily or Monthly

04067500

04059000

0405650004046000

04071765

04069500

04127800

04121970

04122500

0412697004126740

04085427

04086600

04084445

04085200

0410866004087240

04102500

04096015

04093000

Validation Gages

Model DescriptionsARMThe GLERL ARM is a two-step process operating on 121 subbasins in the Great Lakes basin, 27 of which comprise the Lake Michigan basin (Figure 1b) (Croley II & Hartmann 1986; Croley II & He 2002). The first step applies the ARM in partially gaged subbasins (on each day), and the second step is to extrapolate from these partially gaged subbasins to totally ungaged basins by applying ARM a second time. Time series of subbasin monthly runoff estimates are available online, and span the period of 1898-2010 (http://www.glerl.noaa.gov/). Additionally, ARM simulations provided the synthetic subbasin runoff time series that constrained calibration of the Large Basin Runoff Model.

AFINCHAFINCH (described by Holtschlag 2009) was developed by USGS to estimate streamflows and water yields throughout large regions as part of the Great Lakes Basin Pilot Project of the National Water Availability and Use Program. The model simulates monthly flow in each NHDplus flowline (Figure 1c) using step-wise linear regression models relating monthly water yield observations to geospatial climate and land-cover data. The model is configured to incorporate water-use data, and can be constrained to observations at gaged flowlines.

LBRMLBRM (Croley II & He 2002) is a lumped parameter conceptual model that simulates water transport through cascading tanks, and provides forecasts of runoff to the Great Lakes Advanced Hydrologic Prediction System (described by Gronewold et al. 2011). The model, which has nine calibrated parameters, remains the only conceptual rainfall-runoff model to be systematically applied to 121 subbasins in the Great Lakes (Figure 1b) (Coon et al. 2011). The nine parameters were calibrated by conditioning the LBRM on a synthetic discharge time series provided by GLERL’s ARM simulations.

CHPSCHPS is a modeling and operational infrastructure designed to be integrated into the NWS Advanced Weather Interactive Processing System (AWIPS), and provides the basis for sharing new and existing models with the broader hydrologic community (Roe et al. 2010). Data import, storage, and display are provided by the Delft Flood Early Warning System (FEWS), and hydrologic and hydraulic models are provided by the NWS and U.S. Army Corps of Engineers (USACE). For the GRIP analysis, CHPS was implemented using the Sacramento Soil Moisture Accounting Model, operating on the hydrologic units in Figure 1d. Model parameters are estimated by calibration using regression models at gaged hydrologic units and by assignment at ungaged units, based on landscape characteristics and proximity.

Four Configurations of MESHEnvironment Canada uses its Modélisation Environmentale Communautaire - Surface Hydrology (MESH) model (Pietroniro et al. 2007), a distributed model combining land surface models with land surface parameterization and hydrologic routing, to forecast runoff to the lakes from both the U.S. and Canadian portions of the basin. The GRIP project will consider four configurations of MESH (Table 2).

Table 2. MESH Configurations.

Configuration CoupledAtmospheric

Forcing resolution

Land Surface Model Routing Model Response Unit Approach

MESH-Standalone 10 arcsec CLASS (10 arcmin)1WATROUTE (10 arcmin)3

Figure 1eGrouped

MEC-MESH X 10 arcsec ISBA (10 arcmin)2WATROUTE (10 arcmin)3

Figure 1eSingle

MESH-HydroSHEDS with high-resolution routing

X 10 arcsec ISBA (10 arcmin) 2

Based on HydroSHEDS (15 arcsec)4

Figure 1f

Single

MESH-HydroSHEDS with land surface and routing

X 3 arcsec ISBA (15 arcsec) 2

Based on HydroSHEDS (15 arcsec)4

Figure 1f

Single

1 Canadian Land Surface Scheme (CLASS) ( Verseghy 2000)2 Interactions between Surface– Biosphere–Atmosphere (ISBA) (Bélair et al. 2003)3 Kouwen (2010)4 Lehner et al. (2006)

Figure 1. (a) Locations of the USGS gages used for the validation component of the project. (b-f) Spatial framework of each model considered in the GRIP-M analysis. (b) LBRM and ARM are lumped parameter and regional regression models, respectively, operating on 27 subbasins in the basin. (c) AFINCH applies a regression model to 31,820 NHDplus flowlines in the basin, constraining flow to observed discharge where gages provide monthly observations. (d) CHPS is a lumped parameter model operating on 211 hydrologic units in the basin. (e-f) MESH is a distributed model configured for (e) a low resolution land surface model (MESH-Standalone and MEC-MESH) or (f) high resolution routing or high resolution routing and land surface models (2 configurations of MESH-HydroSHEDS).

MethodsThe GRIP-M project involves side-by-side comparison of the time series of runoff to Lake Michigan, cumulative runoff to Lake Michigan for a common simulation period, and model skill at 20 validation gages in the basin. Because the analysis takes place within the context of large scale water balance modeling, we selected the 20 validation gages near the coast. These 20 gages are removed from any calibration or simulation procedures during a common validation period (2002-2010), and simulated monthly discharge time series are compared with the observed flow at these gages. For ARM, we consider two alternative simulation methods: (1) using only the area ratio estimated for the subbasin, leaving gaps in the series when no observation is available within the subbasin, and (2) during months for which no observation is recorded, the area ratio of the lake basin is applied to estimate flow at the gage, essentially the second step of the GLERL implementation of ARM.

Preliminary ResultsPreliminary simulations of Lake Michigan inflow are available for ARM, LBRM, AFINCH, MESH-Standalone, and CHPS. Each model simulates similar peak and low flows (Figure 2). However, CHPS and LBRM typically simulate higher flows and MESH-Standalone flows are lower. ARM and AFINCH, which both incorporate gage information, both simulate flows in the middle of the range of model simulations. Although time series simulations may appear similar among the models, differences over time would result in accumulated error in water level simulations drawing on runoff from these models (Figure 3).

Preliminary validation results for CHPS, ARM, AFINCH, and LBRM suggest varying model skill (Figure 4, Figure 5, and Table 3). In general, CHPS and LBRM somewhat over-predict discharge, consistent with their positions on the plot of cumulative runoff (Figure 3). The prediction skill of ARM and AFINCH varies, with generally improved model skill when other gage observations are available within the subbasin. There does not appear to be a systematic under- or over-prediction bias associated with ARM or AFINCH simulations; however absolute bias can be large, especially from simulations produced by ARM2, which uses the basin area ratio when no observation is available within a subbasin.

Table 3. Goodness-of-fit statistics for simulations at the 20 validation gages, following recommendations by Moriasi et al. (2007) and computed with R package HydroGOF (Zambrano-Bigiarini 2011). NSE is the Nash Sutcliffe Efficiency, Percent Bias is the average percent bias (with positive values indicating overestimation), and RSR is the RMSE-observations standard deviation ratio. NSE PBIAS RSRGage ARM1 ARM2 CHPS AFINCH LBRM ARM1 ARM2 CHPS AFINCH LBRM ARM1 ARM2 CHPS AFINCH LBRM04046000* NA 0.32 NA 0.67 0.16 NA 11.10 NA 32.4 64.9 NA 0.82 NA 0.57 0.9104056500* NA 0.24 0.85 0.73 0.63 NA -24.00 -9.90 -19.5 19.5 NA 0.87 0.38 0.51 0.6104059000 0.92 0.92 0.75 0.85 0.71 4.50 4.50 8.30 19.5 23.6 0.28 0.28 0.50 0.38 0.5404067500 1.00 1.00 0.25 0.64 0.67 1.30 1.30 35.10 13.9 21 0.06 0.06 0.86 0.59 0.5704069500 0.99 0.99 0.51 0.99 0.52 2.20 2.20 36.20 2.7 27.2 0.08 0.08 0.70 0.09 0.6904071765 0.94 0.94 0.64 0.95 0.54 5.80 5.80 26.40 5.1 27.2 0.24 0.24 0.59 0.22 0.6704084445* -0.44 -0.18 0.57 0.92 0.67 -38.00 14.70 22.60 1.2 2.4 1.18 1.08 0.65 0.29 0.5704085200* NA 0.19 0.66 0.73 0.48 NA 72.20 18.00 12.9 8.8 NA 0.90 0.58 0.52 0.7204085427 0.47 0.47 0.65 0.74 0.5 43.90 43.90 28.50 16.2 2.2 0.72 0.72 0.59 0.5 0.704086600 0.01 0.01 0.56 0.93 0.73 43.80 43.80 13.40 2.2 6.8 0.99 0.99 0.66 0.26 0.5104087240 0.71 0.71 0.79 0.93 0.17 26.80 26.80 3.60 -2.3 15.9 0.54 0.54 0.46 0.27 0.9104093000 0.49 0.49 0.71 0.4 0.7 5.30 5.30 -15.90 -14.5 -3.7 0.71 0.71 0.53 0.77 0.5504096015 0.53 0.53 0.73 0.64 0.72 12.70 12.70 20.30 -2 3 0.68 0.68 0.52 0.6 0.5304102500 0.67 0.67 0.66 0.64 0.64 -8.50 -8.50 5.70 -12 -3.1 0.57 0.57 0.58 0.6 0.604108660 0.88 0.88 0.88 0.84 0.61 -2.10 -2.10 1.10 -9.9 -8.7 0.35 0.35 0.34 0.39 0.6204121970 0.84 0.84 0.54 0.96 0.75 8.80 8.80 19.60 2.2 11.9 0.39 0.39 0.68 0.19 0.504122500 0.88 0.88 0.72 0.57 0.78 -4.00 -4.00 9.40 3.9 0.2 0.34 0.34 0.53 0.66 0.4604126740* NA -11.11 -1.61 -10.06 -18.47 NA -4.70 -11.70 18.8 44.2 NA 3.47 1.61 3.31 4.404126970* NA -1.34 -0.97 0.06 -5.59 NA 11.70 33.80 2.2 62 NA 1.52 1.40 0.96 2.5604127800* NA -54.68 -0.20 -9.92 -31.14 NA -65.90 6.90 -26.6 -50.6 NA 7.43 1.09 3.29 5.65

* Gages in ARM subbasins for which there is no observation during some period.

Validation Gages

CHPS

ARM and LBRM

Validation Gages Validation Gages

ConclusionsPreliminary results indicate that all models under consideration for the GRIP-M project simulate similar timing of peak and low flows. However, plots of cumulative runoff suggest that biases among the models result in different simulated accumulated depth of runoff to Lake Michigan over time, and preliminary validation at 20 gages suggest varying model skill. Each model was developed for a different purpose (e.g. large scale water balance simulation and forecasting, investigation of impacts of land use and water withdrawals on stream flow, and flood forecasting), and the GRIP-M project is the first to compare these models for use in regional water balance simulation. Future GRIP work will involve investigating the sources of model error and the potential for each model to improve large scale water balance simulations.

Figure 4. Time series of simulated runoff (cms) at the 20 validation gages. Gage locations are shown in Figure 1a.

Figure 5. Spatial representation of the goodness-of-fit statistics for simulations at the 20 validation gages. (a) ARM1 with no simulations when no observations available within the subbasin, (b) ARM2 with simulation provided by basin-wide area ratio when no observations available within the subbasin, (c) CHPS, (d) AFINCH, and (e) LBRM. Gages for which no simulation is provided by a model are shown as black points.

AcknowledgementsThis work was partially completed under a post-doctoral fellowship with the Cooperative Institute for Limnology and Ecosystems Research, awarded under a Cooperative Agreement between the University of Michigan and the NOAA Great Lakes Environmental Research Laboratory. Additional support was provided by NOAA’s Educational Partnership Program.

ReferencesAnderson, E.J., Schwab, D.J. & Lang, G.A., 2010. Real-time hydraulic and hydrodynamic model of the St. Clair River, Lake St. Clair, Detroit River system. Journal of Hydraulic Engineering, 136(8), pp.507–518.

Bélair, S. et al., 2003. Operational Implementation of the ISBA Land Surface Scheme in the Canadian Regional Weather Forecast Model . Part II : Cold Season Results. Journal of Hydrometeorology, 4(2), pp.371–386.

Coon, W.F. et al., 2011. Compilation of watershed models for tributaries to the Great Lakes, United States, as of 2010, and identification of watersheds for future modeling for the Great Lakes Restoration Initiative: U.S. Geological Survey Open-File Report 2011-1202, Reston, VA: U.S. Department of the Interior, U.S. Geological Survey. Available at: http://pubs.usgs.gov/of/2011/1202.

Croley II, T.E. & Hartmann, H.C., 1986. NOAA Technical Memorandum ERL GLERL-61: Near-Real-Time Forecasting of Large-Lake Water Supplies; A User’s Manual, Ann Arbor, MI.

Croley II, T.E. & He, C., 2002. Great Lakes Large Basin Runoff Modeling. In Second Federal Interagency Hydrologic Modeling Conference, Subcommittee on Hydrology of the Interagency Advisory Committee on Water Data. Las Vegas, NV.

Gronewold, A.D. et al., 2011. An appraisal of the Great Lakes advanced hydrologic prediction system. Journal of Great Lakes Research, 37(3), pp.577–583. Available at: http://linkinghub.elsevier.com/retrieve/pii/S0380133011001638 [Accessed March 20, 2012].

Holtschlag, D.J., 2009. Scientific Investigations Report 2009-5188: Application Guide for AFINCH (Analysis of Flows in Networks of Channels) Described by NHDPlus, Scientific Investigations Report 2009–5188, Reston, VA. Available at: http://pubs.usgs.gov/sir/2009/5188/ [Accessed May 24, 2012].

Kouwen, Nicholas, 2010. WATFLOOD/WATROUTE Hydrological Model Routing & Flow Forecasting System, Waterloo, ON: Department of Civil Engineering, University of Waterloo.

Lehner, B., Verdin, K. & Jarvis, A., 2006. HydroSHEDS Technical Documentation Version 1.0.

Moriasi, D.N. et al., 2007. Model evaluation guidelines for systematic quantification of accuracy in watershed simulations. Transactions of the American Society of Agricultural and Biological Engineers, 50(3), pp.885–900.

Pietroniro, A. et al., 2007. Development of the MESH modelling system for hydrological ensemble forecasting of the Laurentian Great Lakes at the regional scale. Hydrology and Earth System Sciences, 11(4), pp.1279–1294. Available at: http://www.hydrol-earth-syst-sci.net/11/1279/2007/.

Roe, J. et al., 2010. Paper 7B.3: Introduction of NOAA’s Community Hydrologic Prediction System. In 26th Conference on Interactive Information and Processing Systems (IIPS) for Meteorology, Oceanography, and Hydrology. Atlanta, GA.

Verseghy, D.L., 2000. The Canadian land surface scheme (CLASS): Its history and future. Atmosphere-Ocean, 31(1), pp.1–13.

Zambrano-Bigiarini, M., 2011. hydroGOF: Goodness-of-fit functions for comparison of simulated and observed hydrological time series. R package version 0.3-2. Available at: http://cran.r-project.org/package=hydroGOF.

a b c

d e f

Neg PBIASARM1

-38 - -24

-23 - -9

-8 - -4

-3 - 0

Pos PBIASARM1

1 - 2

3 - 6

7 - 13

14 - 27

28 - 44

RSRARM1

0.06 - 0.30

0.31 - 0.50

0.51 - 0.70

0.71 - 1.00

1.01 - 1.18

NSEARM1

-0.44 - 0.00

0.01 - 0.50

0.51 - 0.70

0.71 - 0.90

0.91 - 1.00

Neg PBIASARM2

-66 - 50

51 - -24

-23 - -9

-8 - -4

-3 - 0

Pos PBIASARM2

1 - 2

3 - 9

10 - 15

16 - 27

28 - 72

RSRARM2

0.06 - 0.30

0.31 - 0.50

0.51 - 0.70

0.71 - 1.00

1.01 - 7.43

NSEARM2

-54.68 - 0.00

0.01 - 0.50

0.51 - 0.70

0.71 - 0.90

0.91 - 1.00

a b

Neg PBIASCHPS

-16 - -9

Pos PBIASCHPS

1 - 2

3 - 9

10 - 15

16 - 27

28 - 37

RSRCHPS

0.34 - 0.50

0.51 - 0.70

0.71 - 1.00

1.01 - 1.61

NSECHPS

-1.61 - 0.00

0.01 - 0.50

0.51 - 0.70

0.71 - 0.90

0.91 - 1.00

c

Neg PBIASAFINCH

-27 - -24

-23 - -9

-8 - -4

-3 - 0

Pos PBIASAFINCH

1 - 2

3 - 6

7 - 13

14 - 27

28 - 32

RSRAFINCH

0.09 - 0.30

0.31 - 0.50

0.51 - 0.70

0.71 - 1.00

1.01 - 3.31

NSEAFINCH

-10.06 - 0.00

0.01 - 0.50

0.51 - 0.70

0.71 - 0.90

0.91 - 1.00

Pos PBIASLBRM

-51 - -24

-23 - -9

-8 - -4

-3 - 0

Neg PBIASLBRM

0 - 2

3 - 6

7 - 13

14 - 27

28 - 65

RSRLBRM

0.46 - 0.50

0.51 - 0.70

0.71 - 1.00

1.01 - 5.65

NSELBRM

-31.14 - 0.00

0.01 - 0.50

0.51 - 0.70

0.71 - 0.78

d e

EnvironmentCanada

EnvironnementCanada

Great Lakes Environmental Research LaboratoryGLERL

WEATHER

NATION

AL

SE

RV

IC

E

ARMLBRMMESH StandaloneCHPSAFINCH

1000

2000

3000

1940

s

1000

2000

3000

1950

s

1000

2000

3000

1960

s

1000

2000

3000

1970

s

1000

2000

3000

1980

s

1000

2000

3000

1990

s

..0 ..1 ..2 ..3 ..4 ..5 ..6 ..7 ..8 ..9 ..0

1000

2000

3000

2000

s

Dis

char

ge (c

ms)

Figure 2. Preliminary time series of simulated runoff.

Figure 3. Cumulative runoff to Lake Michigan for the common simulation period (2004-2010) in units of depth over the lake.

2005 2006 2007 2008 2009 20100

1

2

3

4

month

dept

h (m

)

ARMLBRMMESH StandaloneCHPSAFINCH