Open-File Report 2015–1235
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Name/description |
Abbreviation |
Reference |
Climate models |
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Beijing Normal University Earth System Model |
BNU–ESM |
Ji and others (2014) |
Community Earth System Model with Biogeochemical Cycling Model, Version 1.0 |
CESM1–BGC |
Lindsay and others (2014) |
Centre National de Recherches Météorologique Climatological Model 5 |
CNRM–CM5 |
Voldoire and others (2012) |
Institut Pierre Simon Laplace Climate Model 5A, Low-Resolution |
IPSL–CM5A–LR |
Dufresne and others (2013) |
Norwegian Earth System Model, Intermediate Resolution |
NorESM1–M |
Bentsen and others (2013) |
Greenhouse-gas emissions scenarios |
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Representative Concentration Pathway 4.5 |
RCP 4.5 |
Thomson and others (2011) |
Representative Concentration Pathway 8.5 |
RCP 8.5 |
Riahi and others (2011) |
Time periods |
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Average from 2025 to 2049 |
2025–2049 |
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Average from 2050 to 2074 |
2050–2074 |
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Average from 2075 to 2099 |
2075–2099 |
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According to this approach, the key variable that will govern the change in peak flows is the exponent of either precipitation or runoff in the regression equations. If this exponent is greater than one, then peak flows will increase by a relative amount that is greater than the relative increase in precipitation or runoff. The opposite will occur if the exponent is less than one. For example, if precipitation in region 1 of New York increases by 10 percent in a future climate scenario, then the 50-year recurrence-interval peak flow will increase by 11.38 percent because the exponent of the precipitation variable for this region and flow is 1.131 (table 1; Lumia and others, 2006).
Several additional simplifying assumptions were made in the development of this Web-based tool. A broad assumption is that the relation between annual precipitation or runoff and the magnitudes of peak flows will be the same in the future as these values were over the time periods for which the regression equations were developed. These relations were developed based on an analysis of all pertinent and available streamgage discharge data in New York through 1999 (Lumia and others, 2006) and in Vermont through 2011 (Olson, 2014). Discharge data from surrounding States and Canadian Provinces were also used in developing these relations. Several analyses of historical climate data and projections of future climate based on model output have indicated that the magnitude and frequency of large precipitation events is increasing (Groisman and others, 2005; Hodgkins and Dudley, 2011) and is likely to further increase in the future (Toreti and others, 2013; Jannssen and others, 2014). These and other analyses suggest that the relation between annual precipitation and runoff and the size and intensity of large precipitation events may change in the future (Silliman and others, 2013). The development of this Web-based application necessitated the use of the available regression equations, which consider only annual values of precipitation or runoff.
Another important assumption made in the development of this Web-based application is applicable to the peak flow regression equations developed for hydrologic regions 2, 3, 4, and 6 in New York, which use annual runoff as the climatological variable. These annual runoff values are based on the hydrologic analysis of Randall (1996) from 1951 to 1980. Annual runoff is the difference between annual precipitation and annual evapotranspiration (ET) in the absence of changes in water storage or major human alteration of the water cycle in a basin. Recent reports have indicated that ET is increasing in the Northern Hemisphere and that continued increases are likely during the 21st-century (Miralles and others, 2014); however, some conflicting evidence has shown that changes in ET are complex, of high spatial variability, and likely to be influenced by multi-decadal climate oscillations (Jung and others, 2010). In this Web-based application, the ET-to-precipitation ratio is held constant and future changes in annual runoff are governed by changes in precipitation and resulting changes in ET. The effects of future changes in ET on the magnitude of peak flows are not well known at present but are likely to be substantial based on analyses of the role of low soil moisture in moderating the hydrologic impact of past large precipitation events (Ivancic and Shaw, 2015).
A final assumption is pertinent only to the regression equations for region 3 in New York. In this region, the median maximum seasonal snow depth is one of the predictive variables in the regression (Lumia and others, 2006). Future snowfall and snowpack depth for region 3, which includes the Catskill Mountains, is expected to decrease during the 21st-century as the climate warms (Matonse and others, 2013). The effects of a decreasing snowpack on floods in this region are not well known and were not considered in the development of this Web-based application.
This application has several sources of uncertainty, which in total are difficult to quantify and are discussed below. The recommendation is to use this tool in an exploratory manner and to consider the results along with other sources of information to decide how future climate change may affect peak flow magnitudes. This field of investigation is evolving rapidly, and new and better applications and approaches are likely to emerge in the future.
The peak flow regression equations implemented in StreamStats are not readily applicable to two types of watersheds: (1) those that are greatly affected by stream regulation such as reservoirs and (or) by withdrawals or additions for water supply or irrigation and (2) those where urban land use exceeds 15 percent of basin area (Lumia and others, 2006). None of the basins in Vermont are considered urbanized (Olson, 2014).
The user of this Web-based application is encouraged to first obtain a table of basin characteristics from StreamStats before considering how climate change may affect flood magnitudes. Note that the current application provides a percent urban land-area value for any delineated basin reported as “Percentage of land-use from NLCD 2011 classes 21-24.” Regression-based estimates of current peak flow magnitudes for any basin with substantial regulation or diversion or for urban land that covers more than 15 percent of basin area are considered to have unacceptably high uncertainty, indicating that estimates of future peak flow magnitudes in such basins will also have unacceptably high uncertainty. Methods for estimating peak flows in ungaged urban watersheds are described by Sauer and others (1983).
Another reason to explore a delineated basin in StreamStats before applying this new Web-based application is that some basins have geomorphic or land-cover characteristics, including basin drainage area, that are outside the linear range used to develop the peak flow regression equations in each region of New York or in Vermont. StreamStats provides a warning when an out-of-range basin has been delineated, and estimated flood magnitudes from such basins are considered to be poorly defined and should be used with extreme caution (Lumia and others, 2006). Lastly, the current climate explorer Web application requires that delineation points lie within hydrologic regions defined by Lumia and others (2006). For this reason, the stream delineation point (also termed “pourpoint”) cannot be in Pennsylvania, Canada, or offshore in the Great Lakes.
There are several sources of uncertainty in the use of a regression-based approach to estimate peak flow magnitudes, especially when the role of future climate is being considered. The uncertainty of current [in this case, 1999 for New York and 2011 for Vermont] peak flow magnitude estimates can be obtained by using the standard error of prediction of the regression equations for each region of New York as described by Lumia and others (2006) and for Vermont as described by Olson (2014). Other sources of uncertainty in current peak flow estimates arise from inaccuracies in the basin delineation and in the predictive variables.
The application of regression equations derived from spatial analysis to climate change involves a space-for-time substitution. First, the regression equations indicate associations only and not physical processes, so changes in future hydrologic processes, such as runoff, may not be adequately represented in the set of predictive variables in each regression equation as used in this original version of the Web-based application. Second, the regression equations were developed for a 20th-century climate regime that may not adequately reflect the changes in temperature, precipitation, and snowfall patterns that are forecast for the 21st-century. These challenges to this statistical approach indicate a need to devise strategies for testing these regression equations in a climate-change context. At the time of development of the Web-based application, this approach had not yet been adequately tested or validated.
Considerable uncertainty also results from the assumptions and calculations embedded in each climate model and greenhouse-gas scenario. This source of uncertainty is difficult to evaluate; however, one approach has been to examine the ensemble of results available from various climate models and greenhouse-gas scenarios. This application has been designed to provide ensemble peak flow estimates reported as the mean, median, maximum, and minimum values for each selected combination of greenhouse-gas scenario and future 21st-century period for a given delineated basin. A final major source of uncertainty derives from the approach used for downscaling results from global climate models that have a spatial resolution of about 50 to 500 kilometers (Taylor and others, 2012) to the scale of 30 arc-seconds for the data used in this application. This source of uncertainty is potentially large but difficult to quantify (Mearns and others, 2014). The approach used to derive the NEX–DCP30 downscaled dataset can be broadly described as a statistical approach, as described by Thrasher and others (2013) and the National Aeronautics and Space Administration (2013).
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Groisman, P.Y., Knight, R.V., Easterling, D.R., Karl, T.R., Hegerl, G.C., and Razuvaev, V.N., 2005, Trends in intense precipitation in the climate record: Journal of Climate, v. 18, p. 1326–1350.
Guilbert, Justin, Beckage, Brian, Winter, J.M., Horton, R.M., Perkins, Timothy, and Bomblies, Arne, 2014, Impacts of projected climate change over the Lake Champlain basin in Vermont: Journal of Applied Meteorology and Climatology, v. 53, p. 1861–1875.
Gyawali, Rabi, Griffis, V.W., Watkins, D.W., and Fennessey, N.M., 2015, Regional regression models for hydro-climate change impact assessment: Hydrological Processes, v. 29, p. 1972–1985.
Hodgkins, G.A., and Dudley, R.A., 2011, Historical summer base flow and stormflow trends for New England rivers: Water Resources Research, v. 47, no. 7, paper W07528, 16 p., accessed Nover,ber 15, 2015, at https://dx.doi.org/10.1029/2010WR009109.
Ivancic, T.J., and Shaw, S.B., 2015, Examining why trends in very heavy precipitation should not be mistaken for trends in very high river discharge: Climatic Change, v. 133, no. 4, p. 681–693.
Jannssen, Emily, Wuebbles, D.J., Kunkel, K.E., Olsen, S.C., and Goodman, Alex, 2014, Observational- and model-based trends and projections of extreme precipitation over the contiguous United States: Earth’s Future, v. 2, no. 2, p. 99–113.
Ji, D., Wang, L., Feng, J., Wu, Q., Cheng, H., Zhang, Q., Yang, J., Dong, W., Dai, Y., Gong, D., Zhang, R.-H., Wang, X., Liu, J., Moore, J. C., Chen, D., and Zhou, M., 2014, Description and basic evaluation of Beijing Normal University earth system model (BNU–ESM) version 1: Geoscientific Model Development, v. 7, p. 2039–2064.
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Lindsay, Keith, Bonan, G.B., Doney, S.C., Hoffman, F.M., Lawrence, D.M., Long, M.C., Mahowald, N.M., Moore, J.K., Randerson, J.T., and Thornton, P.E., 2014, Preindustrial control and 20th century carbon cycle experiments with the earth system model CESM1 (BGC): Journal of Climate, v. 27, no. 24, p. 8981–9005.
Liu, Ganming, and Schwartz, F.W., 2012, Climate-driven variability in lake and wetland distribution across the Prairie Pothole region—From modern observations to long-term reconstructions with space-for-time substitution: Water Resources Research, v. 48, no. 8, paper W08526, 11 p., accessed October 16, 2015, at https://dx.doi.org/10.1029/2011WR011539.
Lumia, Richard, Freehafer, D.A., and Smith, M.J., 2006, Magnitude and frequency of floods in New York: U.S. Geological Survey Scientific Investigations Report 2006–5112, 152 p.
Matonse, A.H., Pierson, D.C., Frei, Allan, Zion, M.A., Anandhi, Aavudai, Schneiderman, Elliot, and Wright, Ben, 2013, Investigating the impact of climate change on New York City’s primary water supply: Climatic Change, v. 116, nos. 3–4, p. 437–456.
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National Aeronautics and Space Administration, 2013, NEX–DCP30—Downscaled 30 arc-second CMIP5 climate projections for studies of climate change impacts in the United States: National Aeronautics and Space Administration tech note, April 26, 10 p., accessed November 19, 2015, at https://cds.nccs.nasa.gov/wp-content/uploads/2014/04/NEX-DCP30_Tech_Note_v0.pdf.
Olson, S.A., 2014, Estimation of flood discharges at selected annual exceedance probabilities for unregulated, rural streams in Vermont, with a section on Vermont regional skew regression by Veilleux, A.G.: U.S. Geological Survey Scientific Investigations Report 2014–5078, 27 p., appendixes, accessed October 16, 2015, at https://dx.doi.org/10.3133/sir20145078.
Randall, A.D., 1996, Mean annual runoff, precipitation, and evapotranspiration in the glaciated northeastern United States, 1951–80: U.S. Geological Survey Open-File Report 96–395, 2 sheets. [Also available at http://pubs.er.usgs.gov/publication/ofr96395.]
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Silliman, J., Kharin, V.V., Zwiers, F.W., Zhang, X., and Bronaugh, D., 2013, Climate extremes indices in the CMIP5 multimodel ensemble—Part 2—Future climate projections: Journal of Geophysical Research Atmospheres, v. 118, no. 6, p. 2473–2493.
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Thomson, A.M., Calvin, K.V., Smith, S.J., Kyle, G.P., Volke, April, Patel, Pralit, Delgado-Arias, Sabrina, Bond-Lamberty, Ben, Wise, M.A., Clarke, L.E., and Edmonds, J.A., 2011, RCP4.5—A pathway for stabilization of radiative forcing by 2100: Climatic Change, v. 109, no. 4, p. 77–94.
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First posted December 31, 2015
For additional information, contact:
Director, New York Water Science Center
U.S. Geological Survey
425 Jordan Road
Troy, NY 12180
(518) 285-5600
http://ny.water.usgs.gov
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Burns, D.A., Smith, M.J., and Freehafer, D.A., 2015, Development of flood regressions and climate change scenarios to explore estimates of future peak flows: U.S. Geological Survey Open-File Report 2015–1235, 11 p., https://dx.doi.org/10.3133/ofr20151235.
ISSN 2331-1258 (online)