1 U.S. Geological Survey, Lawrence, KS
2 U.S. Geological Survey, Denver, CO
Please direct correspondence to:
David M. Wolock
U.S. Geological Survey
4821 Quail Crest Place
Lawrence, KS 66049
Internet: dwolock@usgs.gov
Phone: (913) 832-3528
FAX: (913) 832-3500
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Citation:
Wolock, D.M. and G.J. McCabe, 1999, Estimates of runoff using water-balance
and atmospheric general circulation models, J. American Water Resources
Assn., 35(6), 1341-1350.
Abstract
Introduction
General Approach
Historical Measured Climate Data
General Circulation Model Data
Estimation of Mean Annual Runoff
Estimation of Uncertainty
Uncertainty Due to Decade-to-Decade Variability
in GCM-Based Mean Annual Runoff
Uncertainty Due to Errors in GCM-Based Runoff
Uncertainty Due to Differences Among the GCMs
Estimated Changes in Runoff
Conclusions and Implications
Literature Cited
Mean annual runoff is defined here as the average amount of water flowing through streams and rivers during a year expressed on a per-unit-area basis. For example, if a watershed with area A yields a volume of water V at its outlet during a year, then the annual runoff for the watershed is V/A; the average over a number of years is the mean annual runoff. Mean annual runoff is an important component of the national assessment because it represents the renewable supply of water. Mean annual runoff is sensitive to variability in climate (Wolock and McCabe, 1999) and, therefore, is a good indicator of how climate change may affect resources dependent on water.
In this paper, the effects of potential climate change on mean annual runoff in the conterminous US are examined using a simple water-balance model and output from two atmospheric general circulation models (GCMs). The objectives of the study described herein are to:
The VEMAP-gridded monthly climate data for the 1961-90 historical baseline were averaged within each of the U.S. Geological Survey's 2,100 water-resources cataloging units in the conterminous US (Figure 1A). The water-balance model then was used with the climate data to estimate mean annual runoff for each cataloging unit. The cataloging-unit runoff values then were averaged within each of the Survey's 18 water-resources regions (Figure 1B) in the conterminous US to provide mean annual runoff values for baseline climate conditions.
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Figure 1. (A) Water-resources cataloging units (8-digit hydrologic
units) and (B) water-resources regions (2-digit hydrologic units).
The VEMAP-gridded monthly climate data also were averaged for 1951-80 within each of the water-resources cataloging units. These data were used as inputs to the water-balance model and the subsequent estimates of mean annual runoff were averaged within each of the 18 water-resources regions. The time period 1951-80 was chosen so that the estimated runoff values could be compared with measured runoff data for the same period derived from the contour map produced by Gebert et al. (1987). (See section on "Estimation of Mean Annual Runoff").
CCC and HAD GCM simulations of future climate were interpolated to the 0.5- by 0.5-deg VEMAP grid (Kittel et al., 1995). The VEMAP-gridded monthly climate data for the periods 2025-34 and 2090-99 were averaged separately within each of the 2,100 water-resources cataloging units (Figure 1A). The water-balance model then was used with each climate data set to estimate mean annual runoff for each cataloging unit. The cataloging-unit runoff values then were averaged within each of the 18 water-resources regions in the conterminous US to provide estimates of mean annual runoff for future climate conditions (Figure 1B).
CCC and HAD GCM simulations of historical climate (not interpolated to the VEMAP grid) also were used in this study. GCM-based monthly temperature and precipitation were averaged within each of the 18 water-resources regions for each month in the period 1901-90. The water-balance model then was used with each GCM historical climate data set to estimate mean annual runoff for each water-resources region for each decade in the period 1901-90. Mean annual runoff results based on the historical GCM simulations were used to estimate uncertainty in the GCM simulations. (See section on "Estimation of Uncertainty").
To evaluate the model's reliability to estimate mean annual runoff for the 18 water-resources regions in the conterminous US, VEMAP-gridded monthly climate data for 1951-80 were used in conjunction with the water-balance model to estimate mean annual runoff. These estimated runoff data were compared with measured runoff data for the water-resources regions for the same period derived from the contour map produced by Gebert et al. (1987). Results of this analysis indicated that the water-balance model reasonably simulates measured mean annual runoff for most of the water-resources regions (Table 1, Figure 2). The correlation coefficient between the measured and estimated mean annual runoff among the regions was 0.98, and the root mean square error was 33 millimeters (12 percent of the mean annual runoff averaged for all 18 water-resources regions). Although the water-balance model reasonably estimates mean annual runoff across the conterminous US, the model underestimates measured runoff in 16 of the 18 water-resources regions. This bias is a significant percentage of the measured runoff in regions with low measured mean annual runoff, such as the Rio Grande and the Great Basin regions. The model bias may reflect some conceptual inadequacy, but it is more likely due to precipitation input data errors (Wolock and McCabe, 1999).
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Table 1. Measured and estimated mean annual runoff.

Figure 2. Measured and estimated mean annual runoff for the 18
water-resources regions in the conterminous United States for 1951-80.
Variability in GCM-based mean annual runoff was estimated by first computing mean annual runoff for each decade during 1901-90 using the CCC and HAD GCM estimates of historical monthly temperature and precipitation for each of the water-resources regions. (There was no trend in GCM-based mean annual runoff for either GCM during 1901-90.) The variability in GCM-based mean annual runoff then was computed as the standard deviation of mean annual runoff estimated for each of the nine decades during 1901-90 (Table 2). Variability in GCM-based mean annual runoff for the CCC model was lowest for the Lower Colorado, California, Arkansas-White-Red, and Souris-Red-Rainy water-resources regions and highest for the Tennessee, South Atlantic-Gulf, Mid Atlantic, Ohio, and Lower Mississippi regions. Variability in GCM-based mean annual runoff for the HAD model was lowest in the Lower Colorado, Upper Colorado, Souris-Red-Rainy, and Arkansas-White-Red water-resources regions and highest in the Tennessee, Ohio, California, and South Atlantic-Gulf water-resources regions.
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Table 2. Estimates of uncertainty in GCM-based mean annual runoff.
The differences in decade-to-decade runoff variability among water-resources regions and between the GCMs reflect differences in variability in precipitation. Precipitation is the primary factor that determines estimated runoff. (See the section on "Estimated Changes in Runoff"). Therefore, differences in precipitation variability will cause differences in runoff variability.
The variability in GCM-based mean annual runoff was used to determine the
statistical significance (at
= 0.05) of the
GCM-simulated changes in mean annual runoff estimated for future periods
(2025-34 or 2090-99) using a two-tailed t-test. The test statistic was
computed as:
where t is the test statistic,
is the
change in mean annual runoff from the baseline climate (1961-90) to one of
the climate-change decades (2025-34 or 2090-99), and s is the standard
deviation of mean annual runoff estimated for 1901-90. The term
is required in the denominator
because a one decade period (2025-34 or 2090-99) is compared to a three
decade period (1961-90). t and
are
estimated for each combination of GCM (CCC or HAD) and climate-change decade
(2025-34 or 2090-99), and s is estimated for each GCM. Changes in
GCM-simulated mean annual runoff not significant at
= 0.05 were considered uncertain (or at least
smaller than GCM-based decade-to-decade runoff variability).
The CCC and HAD GCMs produced similar spatial patterns of error in GCM-based runoff (Table 2). In general, both models underestimate mean annual runoff in the Lower Mississippi and Tennessee water-resources regions and overestimate runoff in the Pacific Northwest, Great Basin, Upper Colorado, California, Mid Atlantic, and Missouri water-resources regions. In absolute terms, the errors in CCC-based runoff mostly were larger than the errors in HAD-based runoff.
The spatial patterns of error in CCC- and HAD-based runoff are caused by errors in GCM-based precipitation estimated for 1961-90 (data not shown). The GCMs underestimate (or overestimate) measured mean annual runoff in regions where they underestimate (or overestimate) measured mean annual precipitation. These biases in GCM-estimated precipitation are consistent with wet and dry biases reported by Doherty and Mearns (1999).

Table 3. Estimated mean annual runoff and changes in runoff.
The changes in runoff that are based on the GCM-estimated climate changes mostly were associated with GCM-estimated changes in precipitation (Figure 3). The differences in estimated changes in mean annual runoff between the GCMs and the differences in estimated changes among the water-resources regions primarily are related to differences in estimated changes in precipitation. The Pearson correlation coefficient for the relation between changes in runoff and changes in precipitation was 0.87. Changes in temperature, which are reflected by changes in potential evapotranspiration, had a less important effect on changes in mean annual runoff (correlation coefficient = -0.26).
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Figure 3. Changes in mean annual runoff, mean annual precipitation,
and mean annual potential evapotranspiration from historical baseline
(1961-90) to future GCM-simulated climate conditions. The results are for
GCMs from the Canadian Centre for Climate Prediction and Research (CCC) and
Hadley Centre for Climate Prediction and Research (HAD).
The CCC and HAD GCMs predict different changes in precipitation because they are different mathematical representations of the hydrologic cycle. The two models differ in their spatial and conceptual complexity, and they are parameterized differently (Felzer and Heard, in review). The HAD model is more complex than the CCC model, but this does not necessarily imply that the HAD model estimates of future climate are more correct.
For the 2025-34 decade, the absolute magnitudes of the simulated changes in runoff were greater than variability in GCM-based mean annual runoff in only 3 of the 18 water-resources regions for the CCC model and in none of the water-resources regions for the HAD model (Table 4). Thus, most of the CCC-estimated changes in runoff and all of the HAD-based changes in runoff for 2025-34 were within the background "noise" level of decade-to-decade variability in mean annual runoff.
In addition, the 2025-34 decade changes in runoff were greater than the error in the GCM-based mean annual runoff in only 4 of the 18 water-resources regions for the CCC model and in only 4 regions when the HAD model was used (Table 4). These results show that the GCM-based changes in mean annual runoff are less than the expected error in the simulations for the majority of the water-resources regions for both GCMs.

Table 4. Uncertainty tests for the 2025-34 changes in runoff (-
indicates a significant decrease, and + indicates a significant increase in
mean annual runoff).
The 2025-34 decade changes in mean annual runoff were in the same direction for five water-resources regions (Table 4). When all three sources of uncertainty are considered (variability in GCM-based mean annual runoff, error in the GCM-based mean annual runoff, and disagreement in direction of change between the two GCMs), then the changes in mean annual runoff for all the water-resources regions would be considered uncertain.
For the 2090-99 decade, the absolute magnitude of the simulated changes in runoff was greater than variability in GCM-based mean annual runoff in only 4 of the 18 water-resources regions for the CCC model and in 8 of the water-resources regions for the HAD model (Table 5). The 2090-99 decade changes in runoff were greater than the error in the GCM-based mean annual runoff for 5 of the 18 water-resources regions for the CCC model and for 10 of the water-resources regions for the HAD model (Table 5).

Table 5. Uncertainty tests for the 2090-99 changes in runoff (-
indicates a significant decrease, and + indicates a significant increase in
mean annual runoff).
The 2090-99 decade changes in mean annual runoff were in the same direction for both GCMs in seven water-resources regions (Table 5). When all three sources of uncertainty are considered (variability in GCM-based mean annual runoff, error in the GCM-based mean annual runoff, and disagreement in direction of change between the two GCMs), then the changes in mean annual runoff would be considered uncertain in all but one (California) water-resources region. It cannot be concluded, however, that a future increase in mean annual runoff for the California water-resources region is a certain outcome. Analysis of future climate conditions predicted by other GCMs could yield very different results.
The effects of climate change on mean annual runoff cannot be estimated reliably because of uncertainty related to GCMs. Most atmospheric scientists believe that GCMs will become more reliable as their spatial and conceptual complexity continue to improve. The level of adequate detail and the time when that will be achieved, however, are unresolved issues. Until the large uncertainty associated with GCM-simulations of future climate can be resolved, a useful path for future research is sensitivity analyses using a range of changes in temperature and precipitation. Such analyses can be used to understand the response of annual runoff (and water resources systems) to climate and to identify important vulnerabities.
Felzer, B., and P. Heard, in review, Hydrological Implications of GCM Results for the U.S. National Assessment, Journal of the American Water Resources Association.
Gebert, W.A., D.J. Graczyk, and W.R. Krug. 1987. Average Annual Runoff in the United States, 1951-80. Hydrol. Invest. Atlas HA-710, U.S. Geological Survey, Reston, VA
Hamon, W.R., 1961. Estimating Potential Evapotranspiration. Journal of the Hydraulics Division, Proceedings of American Society Civil Engineers 87, 107-120.
Johns, T.C., R.E. Carnell, J.F. Crossley, J.M. Gregory, J.F.B. Mitchell, C.A. Senior, S.F.B. Tett, and R.A. Wood, 1997. The Second Hadley Centre Coupled Ocean-Atmosphere GCM: Model Description, Spinup and Validation. Climate Dynamics, 13, 103-134.
Kittel, T.G.F., N.A. Rosenbloom, T.H. Painter, D.S. Schimel and VEMAP Modeling Participants, 1995. The VEMAP Integrated Database for Modeling United States Ecosystem/Vegetation Sensitivity to Climate Change. Journal of Biogeography, 22, 857-862.
U.S. Department of Agriculture, 1993. State Soils Geographic Data Base (STATSGO) Users Guide. Soil Conservation Service, Miscellaneous Publication 1492, 88 pp.
Wolock, D.M., and G.J. McCabe, 1999. Explaining Spatial Variability in Mean Annual Runoff in the Conterminous United States. Climate Research, 11, 149-159.
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