1. Introduction
Increased computational capabilities, the availability of new data sources such as remote sensing, and better understanding of the Earth system have resulted in considerable improvements in the ability to represent long-term variations in land surface water and energy fluxes and state variables. Earth system models require, among other things, consistent observational datasets for model testing and diagnosis. Furthermore, predictions of alternative future scenarios of land surface conditions resulting from changes in climate and/or land cover require benchmark historical data against which to evaluate.
We describe an observational dataset (herein called L13) that provides a means to analyze and verify hydroclimatic predictions as well as to drive land surface models, along with fluxes and state variables from the variable infiltration capacity (VIC) model. The L13 dataset is based on the methods of Maurer et al. (2002; hereafter M02), who developed a set of publicly available gridded meteorological data from ground-based measurements, together with model-derived hydrologically consistent surface fluxes and states. M02 spanned the period 1 January 1949–31 July 2000 (~51.5 yr) at a ⅛° latitude/longitude spatial resolution. The L13 dataset described here refines the spatial resolution to
An examination of the most widely cited studies that reference and/or use the M02 data (in total, over 300 Web of Science citations; http://wokinfo.com/) suggests that the applications can be grouped into three general areas: 1) studies that use the meteorological and hydrological data directly to characterize the state or variability of a specific hydroclimatic variable (e.g., temperature, precipitation, and snowpack), 2) studies that use the data as a spatially and temporally complete observational baseline for downscaling climate model output (especially for bias correction) to generate future climate scenarios, and 3) water and energy balance studies, for which the model forcings and derived fluxes are of particular interest because the derived surface water and energy budgets close at all grid cells at each time step by construct. Examples of each of these applications are discussed below.
Westerling et al. (2006) used the M02 gridded meteorological data along with other sources to isolate the signal of climatic variability on wildfire frequency in the western United States. Hayhoe et al. (2007) used the archived hydrological fluxes and states to represent historical hydrologic conditions from which future meteorological scenarios were assessed via hydrologic simulations in the northeastern United States. Soil moisture data were used by Castro et al. (2007) to initialize a regional climate model to simulate U.S. climatology. Sheffield et al. (2004) used M02 soil moisture to derive a hydrologically based drought index, which showed good agreement with time series of U.S. drought from two Palmer drought severity index (PDSI) datasets.
The second group of studies typically follows procedures that include correcting downscaled climate model output with the M02 forcing data, and then using the bias-corrected model to produce future climatic scenarios. Cayan et al. (2008) and Hayhoe et al. (2004) both exploited the downscaled climate model outputs to assess climatic implications of future greenhouse gas emission scenarios in California using this general approach. Loarie et al. (2008) used downscaled outputs to examine impacts on the diversity of flora in California. Salathé (2003) downscaled climate model outputs to simulate streamflow over a river basin in Washington State and also evaluated performance of several climate models after bias correction. Wood et al. (2004) used the forcing and hydrological datasets to evaluate six bias correction methods for downscaling climate model outputs over the continental United States.
Among the third type of applications, Stewart et al. (2004) utilized the forcing data to simulate streamflow over large river basins in the Pacific Northwest. Smith et al. (2004) used the meteorological data to force a suite of land surface models and compared their performance. Christensen et al. (2004) applied the forcing data over the Colorado River basin to search for robust VIC model parameters over small river basins that were then used to assess climatic impacts under future forcing scenarios. Carpenter and Georgakakos (2004) utilized the energy forcing data to compute potential evapotranspiration (ET) in a radar–rainfall uncertainty study. Maurer et al. (2004) used climate data and the archived VIC-derived soil moisture, snow, and runoff data to examine predictability of runoff across the United States. Andreadis and Lettenmaier (2006) used the forcing data to evaluate a data assimilation scheme using satellite-based snow water equivalent (SWE) information.
Climate model outputs, remote sensing, and land cover data continue to become available at finer spatial resolutions, making the spatial refinement of L13 a significant improvement (from ⅛° to
As in the original M02 dataset, we produced three types of data, all of which are publicly available (http://www.hydro.washington.edu/SurfaceWaterGroup/Data/gridded/index.html): 1) station-based daily precipitation and temperature data, and wind fields from the National Centers for Environmental Prediction (NCEP)–National Center for Atmospheric Research (NCAR) reanalysis (Kalnay et al. 1996); 2) derived subdaily (3 hourly) land surface model forcing data, including precipitation and temperature, as well as downwelling solar and longwave radiation, humidity, and surface air pressure; and 3) model-based hydrological states and fluxes. We attempted as much as possible to follow the methods of M02, so that studies using those data can apply L13 to extend or refine their previous analyses. Below, we briefly describe the spatial gridding methodology and updates to the hydrologic model and provide comparisons between M02 and L13. We also compare model-based hydrologic outputs with observations of streamflow, soil moisture, and surface heat and radiative fluxes, presented here in a format consistent with M02.
2. Gridding methodology
The gridding methods of M02 were closely followed in L13, and the reader may find complete details in that publication. The L13 dataset is derived from observations of precipitation and minimum and maximum daily temperature at National Climatic Data Center (NCDC) Cooperative Observer (COOP) stations across the conterminous United States (DSI-3200). Although the cumulative total number of stations used is about 20 000, the number at any time varies, with a peak of approximately 12 000 stations in 1970. As in M02, we used only stations with at least 20 years of valid data. L13 uses the same relationships as in M02 to estimate those variables (downward solar and longwave radiation and humidity) that are not observed directly using algorithms described in the next paragraph. Both temperature and precipitation were gridded to
Vapor pressure, humidity, and incoming shortwave and longwave radiation were derived using algorithms from mountain microclimate simulator (MTCLIM; Kimball et al. 1997; Thornton and Running 1999; Thornton et al. 2001) as described in M02, with several updates outlined in Bohn et al. (2013) The major difference between the version of MTCLIM used in L13 and M02 is a change in the estimate of longwave radiation from Tennessee Valley Authority (1972) to Prata (1996). To provide subdaily (3 hourly) temperature, a spline was applied to daily minimum and maximum temperatures to estimate the diurnal cycle (see Bohn et al. 2013).
Hydrologic model
As in M02, hydrologic states and fluxes were simulated using the VIC model (Liang et al. 1994). VIC is a grid-based hydrologic model that balances surface energy and water budgets at typical spatial resolutions ranging from a few to hundreds of kilometers. VIC represents subgrid variability of vegetation and runoff generation, while also accounting for subgrid topography through elevation bands. Land-cover input data are the same as in M02, with static vegetation (Hansen et al. 2000), and soil information (Miller and White 1998) aggregated from a 1-km database for the effective years of 2000 and 1998, respectively. The VIC model used in L13, version 4.1.2, was run in energy balance mode, and has undergone a number of upgrades since the M02 data were published (using version 4.0.3). Readers are referred to the VIC website (http://www.hydro.washington.edu/Lettenmaier/Models/VIC/) for a complete description of these upgrades, the most important of which are related to the snow accumulation and ablation model, which now performs a separate energy balance for canopy snowpack and snow on the ground (Andreadis et al. 2009).
3. Evaluation
We first compared gridded station data from L13 and M02 (Fig. 1) for summer and winter over the concurrent period from 1 January 1950 to 31 July 2000. The two datasets are largely consistent, with differences mainly over topographically complex regions in the western United States. The major source of discrepancies are 1) intragrid variability from the four

L13 minus M02 for (top) summer [June–August (JJA)] and (bottom) winter [December–February (DJF)] mean monthly (left) precipitation, (center) max temperature, and (right) min temperature for the concurrent period (1 Jan 1950–31 Jul 2000).
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1

L13 minus M02 for (top) summer [June–August (JJA)] and (bottom) winter [December–February (DJF)] mean monthly (left) precipitation, (center) max temperature, and (right) min temperature for the concurrent period (1 Jan 1950–31 Jul 2000).
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1
L13 minus M02 for (top) summer [June–August (JJA)] and (bottom) winter [December–February (DJF)] mean monthly (left) precipitation, (center) max temperature, and (right) min temperature for the concurrent period (1 Jan 1950–31 Jul 2000).
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1
Figure 2 compares derived surface energy budget components with observations from four Ameriflux towers during summer (see Table 1). Simulated fluxes track observations fairly well at each site with several exceptions. First, derived fluxes tend to underpredict sensible heat fluxes and overpredict latent heat fluxes. The average difference in latent heat flux across sites and time intervals is −19.5 W m−2, or 17%, which is equivalent to an overestimation of 0.69 mm day−1 of evaporation during summer. Second, at Niwot Ridge (a high-alpine site) there is a timing lag in the simulated peak radiation. Downward solar radiation is a derived quantity based on minimum and maximum daily air temperatures, which suggests that the assigned timing for the

L13 (dashed lines) modeled energy budget components compared with observations (solid lines) for a single summer for each Ameriflux site (JJA), specifically Blodgett Forest, CA (2004); Niwot Ridge, CO (2006); Brookings, SD (2005); and Howland Forest, ME (2001).
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1

L13 (dashed lines) modeled energy budget components compared with observations (solid lines) for a single summer for each Ameriflux site (JJA), specifically Blodgett Forest, CA (2004); Niwot Ridge, CO (2006); Brookings, SD (2005); and Howland Forest, ME (2001).
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1
L13 (dashed lines) modeled energy budget components compared with observations (solid lines) for a single summer for each Ameriflux site (JJA), specifically Blodgett Forest, CA (2004); Niwot Ridge, CO (2006); Brookings, SD (2005); and Howland Forest, ME (2001).
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1
Details of observational Ameriflux data used for comparison with simulated fluxes and states.


Soil moisture plays a central role in hydrologic processes such as runoff generation and ET, and is a key indicator of drought. Simulated soil moisture from VIC, driven as described above, was compared with observations from 19 sensors in Illinois retrieved from the Global Soil Moisture Data Bank (Robock et al. 2000) summarized in Table 2. Figure 3 shows mean monthly soil moisture values as well as the autocorrelations. VIC climatological soil moisture values are consistently lower than the observations for the 19-sensor average. However, the VIC-simulated intermonthly variability tracks very closely with observations, indicating that the model realistically simulates moisture storage changes and water budget dynamics for this part of the domain. The monthly autocorrelation is a measure of persistence of soil moisture anomalies in time, important for seasonal runoff forecasting and characterizing drought evolution. Figure 3b demonstrates that the temporal structure of model response effectively captures observed persistence for the first 3 months, becoming slightly less persistent thereafter, while autocorrelations become almost negligible beyond 5 months. The L13 magnitude and autocorrelations track those from observed soil moisture comparably to the original M02 data.
Details of observational Global Soil Moisture Data Bank data used for comparison with simulated fluxes and states.



Comparison of L13 (a) mean monthly soil moisture and (b) autocorrelations with 19 sensors in Illinois retrieved from the Global Soil Moisture Data Bank (1981–2004) for the top 1 m of soil (observed and modeled soil columns may extend slightly deeper). Note: Bars in (a) indicate monthly std dev.
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1

Comparison of L13 (a) mean monthly soil moisture and (b) autocorrelations with 19 sensors in Illinois retrieved from the Global Soil Moisture Data Bank (1981–2004) for the top 1 m of soil (observed and modeled soil columns may extend slightly deeper). Note: Bars in (a) indicate monthly std dev.
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1
Comparison of L13 (a) mean monthly soil moisture and (b) autocorrelations with 19 sensors in Illinois retrieved from the Global Soil Moisture Data Bank (1981–2004) for the top 1 m of soil (observed and modeled soil columns may extend slightly deeper). Note: Bars in (a) indicate monthly std dev.
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1
In addition to soil moisture, SWE is a key hydrologic state variable. Figure 4 shows histograms of the dynamic soil moisture range, mean and maximum SWE, and precipitation for M02 and L13 over the concurrent time period, as well as L13 for the extended period (1 January 1915–31 December 2011). SWE values were frequently larger for the finer spatial domain (

Cumulative density functions (CDFs) of (left) inputs max and mean daily precipitation and (right) state variables soil moisture and SWE, comparing the historic M02 dataset (solid lines) with the L13 dataset over the concurrent period (1 Jan 1950–31 Jul 2000; dashed lines) and the entire L13 record (1 Jan 1916–31 Dec 2011; dotted lines). Total soil depth is variable across the domain ranging from roughly 1.5 to 2.7 m. Mean and max precipitation are separated for ease of viewing.
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1

Cumulative density functions (CDFs) of (left) inputs max and mean daily precipitation and (right) state variables soil moisture and SWE, comparing the historic M02 dataset (solid lines) with the L13 dataset over the concurrent period (1 Jan 1950–31 Jul 2000; dashed lines) and the entire L13 record (1 Jan 1916–31 Dec 2011; dotted lines). Total soil depth is variable across the domain ranging from roughly 1.5 to 2.7 m. Mean and max precipitation are separated for ease of viewing.
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1
Cumulative density functions (CDFs) of (left) inputs max and mean daily precipitation and (right) state variables soil moisture and SWE, comparing the historic M02 dataset (solid lines) with the L13 dataset over the concurrent period (1 Jan 1950–31 Jul 2000; dashed lines) and the entire L13 record (1 Jan 1916–31 Dec 2011; dotted lines). Total soil depth is variable across the domain ranging from roughly 1.5 to 2.7 m. Mean and max precipitation are separated for ease of viewing.
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1
Simulated streamflows are compared with observations in Fig. 5 from major river basins covering large portions of the domain. For several basins, particularly in the western United States, naturalized streamflow data were obtained that have been adjusted for anthropogenic impacts, including upstream regulation, water withdrawals, and evaporation from upstream reservoirs (see Table 3). Limited VIC parameter estimation was performed to match surface and subsurface runoff from the previously calibrated VIC (version 4.0.3) used in M02. We employed a technique similar to Troy (2008) with the objective of matching the runoff ratio (in this case between model versions 4.0.3 and 4.1.2) at regularly spaced intervals of 1°. A Monte Carlo search consisting of 200 iterations was applied, which varied three VIC soil parameters—the variable infiltration curve parameter b, the maximum velocity of baseflow parameter Dsmax, and the depth of the bottom soil layer D3—within a narrow range (±10%) of their previous values.

Mean monthly hydrographs from L13 (m3 s−1) over the period 1961–90. Simulated flows are denoted by dashed lines, while observed or naturalized flows are solid lines.
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1

Mean monthly hydrographs from L13 (m3 s−1) over the period 1961–90. Simulated flows are denoted by dashed lines, while observed or naturalized flows are solid lines.
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1
Mean monthly hydrographs from L13 (m3 s−1) over the period 1961–90. Simulated flows are denoted by dashed lines, while observed or naturalized flows are solid lines.
Citation: Journal of Climate 26, 23; 10.1175/JCLI-D-12-00508.1
Details of observational streamflow data used for comparison with simulated fluxes and states.


Offline simulations were conducted to evaluate the impact of using climatological winds prior to 1948 (see the supplemental material). These comparisons showed that with few exceptions use of the climatological winds slightly reduce the temporal and spatial variability of hydrologic fluxes but have small relative impacts on long-term mean values. Relative impacts on short-term (3-hourly and daily) values are greatest, and are less at monthly time steps. Given the uncertainty in using static vegetation and soil (from 2000 and 1998, respectively), the derived model outputs for the earlier part of the simulation period serve as a reference scenario (rather than a reconstruction), while providing the necessary meteorological inputs for users who might desire to produce more detailed dynamic reconstructions [as a point of reference, Matheussen et al. (2000) found maximum changes in runoff and ET of less than 10% for reconstructed 1900 versus 1990 vegetation in the Columbia River basin]. Additional uncertainty arises from using a constant lapse rate in regions of topographical complexity (i.e., western United States), with the potential to bias daily temperature range in certain cases, which may impact derived downwelling shortwave radiation based on the MTCLIM algorithm. It follows that undocumented or incomplete QC of instrument change error may hinder the robustness of trends in these data, as pointed out by Menne et al. (2009). Menne et al. (2010) subsequently showed that there has been no successful correction of the biases associated with the change from liquid-in-glass (LiG) thermometers to Maximum–Minimum Temperature System (MMTS) in the daily NCDC station dataset. This is estimated to result in an artificial negative bias in maximum temperatures less than approximately 0.5°C, which would translate into a slight underestimation of diurnal temperature range and reduction in derived shortwave radiation for L13. This instrument bias could have further implications for simulated cold-season processes (snowpack evolution) and surface heat fluxes, as well as for drought assessment and climate-oriented analyses such as downscaling.
4. Data format and availability
The data are available in Network Common Data Form (NetCDF) format, conforming to the Assistance for Land-Surface Modelling Activities (ALMA) convention of Polcher et al. (2000). This means that moisture fluxes are expressed as kilograms per square meter per second, energy fluxes as watts per square meter, and moisture states as kilograms per square meter. (The data are freely accessible from
5. Conclusions
We have described an observation-based hydrologically consistent dataset for the period 1915–2011 at a
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