Influence of modern land cover on the climate of the United States
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I have used a high-resolution nested climate modeling system to test the sensitivity of regional and local climate to the modern non-urban land cover distribution of the continental United States. The dominant climate response is cooling of surface air temperatures, particularly during the warm-season. Areas of statistically significant cooling include areas of the Great Plains where crop/mixed farming has replaced short grass, areas of the Midwest and southern Texas where crop/mixed farming has replaced interrupted forest, and areas of the western United States containing irrigated crops. This statistically significant warm-season cooling is driven by changes in both surface moisture balance and surface albedo, with changes in surface moisture balance dominating in the Great Plains and western United States, changes in surface albedo dominating in the Midwest, and both effects contributing to warm-season cooling over southern Texas. The simulated changes in surface moisture and energy fluxes also influence the warm-season atmospheric dynamics, creating greater moisture availability in the lower atmosphere and enhanced uplift aloft, consistent with the enhanced warm-season precipitation seen in the simulation with modern land cover. The local and regional climate response is of a similar magnitude to that projected for future greenhouse gas concentrations, suggesting that the climatic effects of land cover change should be carefully considered when crafting policies for regulating land use and for managing anthropogenic forcing of the climate system.
KeywordsLand Cover Land Cover Change Surface Albedo Advance Very High Resolution Radiometer Advance Very High Resolution Radiometer
It is now well established that land cover influences surface climate, both through biophysical interactions that affect surface energy balance and through biogeochemical interactions that affect the carbon cycle (Pielke et al. 2002). Biophysical influences are exerted by both human-dominated and “natural” landscapes. For instance, the presence of urban areas causes local heating (e.g., Brazel et al. 2007) and can even alter the path of individual thunderstorms (e.g., Changnon 2001). Likewise, deforestation has been shown to explain observed regional drying in both the tropics (Werth and Avissar 2002) and extratropics (Pitman et al. 2004). It has also been argued that agricultural expansion contributed to northern hemisphere cooling prior to substantial increases in greenhouse gas concentrations (e.g., Govindasamy et al. 2001). Further, even before wide-spread human perturbations of the landscape, land cover change played a key role in shaping regional paleoclimates, with biophysical land cover effects especially important to regional climate sensitivity (e.g., Diffenbaugh and Sloan 2002; Foley et al. 1994; Wyputta and McAvaney 2001).
Here I examine the influence of modern land cover on climate in the continental United States. The mean surface temperature of the earth has increased over the past 160 years, with the steepest warming occurring over the last quarter century (IPCC 2007). This warming has occurred over both land and ocean, with elevated greenhouse gas concentrations being the most likely culprit (IPCC 2007). However, although a number of first-order discrepancies in the instrumental data have been reconciled (e.g., Mears and Wentz 2005; Santer et al. 2008; Sherwood et al. 2005), there remains uncertainty as to how other climate forcings have acted to modify the effects of rising greenhouse gas concentrations, particularly at local and regional scales. For instance, it has been argued that agricultural areas have warmed the surface by increasing the heat capacity of the soil and vegetation (Christy et al. 2006; Kalnay and Cai 2003). Conversely, climate model experiments suggest that agricultural areas have cooled the surface (e.g., Feddema et al. 2005a; Govindasamy et al. 2001; Kueppers et al. 2007; Lobell et al. 2006b), leading to the hypothesis that widespread irrigation has “masked” the global warming signal (Kueppers et al. 2007).
In addition to influences on past climate, changes in land cover resulting from both direct human modification and biogeographic change could have substantial impact on surface climate in the coming decades (e.g., Diffenbaugh 2005a, b; Feddema et al. 2005b; Jackson et al. 2005). In fact, as scientists and policy makers grapple with ways to mitigate potential greenhouse gas-induced changes in climate, climate policy is itself emerging as a potential driver of land cover change (e.g., Fargione et al. 2008; Jackson et al. 2005; Searchinger et al. 2008). We are therefore faced with the possibility that biofuel and sequestration markets (and mandates) could influence climate not only through changes in greenhouse gas concentrations, but also through changes in surface energy and water budgets (e.g., Bala et al. 2007; Betts 2000; Jackson et al. 2005).
Quantifying the influence of biophysical land cover effects is thus critical both for understanding observed changes in the climate system during the recent period of intense human perturbation, and for understanding how the climate system may change in the future. Further, because the response of regional and local climate to land cover forcing could be different than the response to global greenhouse gas forcing (e.g., Diffenbaugh 2005a), and because the influence of land cover is likely to be stronger at local and regional scales than at the global scale (e.g., IPCC 2007), it is imperative that this quantification of biophysical effects be made at fine spatial scales over large continental areas.
2 Models and methods
I have employed the ICTP RegCM3 nested climate model (Pal et al. 2007). RegCM3 successfully captures the climatological patterns of temperature and precipitation over the continental United States (Diffenbaugh et al. 2006). The domain used here follows that of (Diffenbaugh et al. 2005), which covers the full continental United States and surrounding areas with 25 km horizontal grid spacing. The domain has 145 points in the latitude direction and 220 points in the longitude direction, with 18 levels in the vertical. For this grid, the model uses a 75-s time-step.
RegCM3 uses the hydrostatic dynamical core from MM5 (Grell et al. 1994), the radiative transfer package from CCM3 (Kiehl et al. 1996), and the nonlocal countergradient boundary layer scheme of Holtslag et al. (1990). Large-scale (“non-convective”) precipitation is parameterized using the SUBEX physics scheme (Pal et al. 2000). In the simulations reported here, cumulus convection is parameterized using the Grell scheme (Grell 1993), with the Fritsch and Chappell closure assumption (Fritsch and Chappell 1980).
RegCM3 uses the Biosphere–Atmosphere Transfer Scheme (BATS 1e) (Dickinson et al. 1993) to calculate fluxes of energy, momentum and moisture between the land surface and the atmosphere. BATS has one vegetation layer and three soil layers. The vegetation and soil properties are parameterized based on a single land cover designation at each grid point. The phenological variables are prescribed for each land cover type based on fixed parameters, such as minimum leaf area index (LAI), maximum LAI, and maximum fractional vegetation cover, along with the seasonal progression of temperature. The BATS land cover types include parameterizations for both irrigated crop and crop/mixed farming areas. In the irrigated crop areas, root zone soil moisture is set to field capacity throughout the year.
In the experiments reported here, both datasets were gridded to the 25 km RegCM3 grid (Fig. 1). The most prominent difference between the two datasets is the presence of crop types in the GLCC dataset. Large areas of crop/mixed farming are replaced in the RF dataset primarily by short grass in the Great Plains, interrupted forest in the Midwest and southern Texas, and evergreen needleaf trees in the Southeast. Smaller areas of irrigated crop occur in the western United States and are replaced in the RF dataset primarily by various mixtures of interrupted forest, short grass, evergreen shrubs, and semidesert.
I have conducted two climate model integrations covering the period 1982–2002, with the NCEP-DOE Reanalysis Product (Kanamitsu et al. 2002) providing large-scale boundary conditions for both integrations. One integration (GLCC) uses the modern non-urban land cover distribution from the GLCC database (Fig. 1a). The other integration (RF) uses the potential vegetation distribution of (Ramankutty and Foley 1999) (Fig. 1b). The land cover types are applied as the bottom boundary condition in RegCM3 with the distribution shown in Fig. 1, using the parameterizations in BATS. Annually-varying greenhouse gas concentrations are prescribed following Schlesinger and Malyshev (2001).
Previous work shows that land surface schemes can require multiple years to equilibrate (Yang et al. 1995). In both integrations, the first 6 years are discarded to account for climate model equilibration, leaving the 15 years from 1988 through 2002 for climate model analysis. I have tested the statistical significance of the mean monthly temperature and precipitation changes using Student’s t test.
Finally, I have used three datasets to identify recent temperature changes in the United States: the Willmott–Matsuura global terrestrial air temperature timeseries (Willmott and Matsuura 2001) (1988–1999), the Climate Research Unit TS 2.0 timeseries (Mitchell and Jones 2005) (1988–2000), and the North American Regional Reanalysis product (Mesinger et al. 2006) (1988–2002).
3.1 Seasonal means
Means (K) and trends (K/decade) of annual surface air temperature in the RF and GLCC simulations (1988–2002)
Areas changed from crop/mixed farm
Areas changed from irrigated crop
Changes in mean monthly surface air temperature and daily maximum temperature are also statistically significant in the warm-season over areas of the western United States designated as irrigated crop in the GLCC simulation (Figs. 1, 6). (The changes are statistically significant over the irrigated areas of the Central Valley of California through October and November, respectively.) In these areas, the GLCC simulation shows increased warm-season surface soil moisture (>8 mm) and evapotranspiration (up to >2.0 mm/day), along with decreased surface net longwave flux (>−20 W/m2) and sensible heat flux (>−40 W/m2). Changes in mean daily minimum temperature are statistically significant over areas of the western United States from March through October (Fig. 6). These areas exhibit warming of daily minimum temperatures in the GLCC simulation where desert was converted to semidesert, decreasing net shortwave flux by up to −12.5 W/m2, while decreasing surface soil moisture by up to −3 mm and evapotranspiration by up to −0.8 mm/day.
3.2 Late twentieth century trends
The three observationally-based datasets each show a positive surface air temperature trend over the late twentieth century period (Climate Research Unit = 0.43 K/decade, Willmott–Matsuura = 0.52 K/decade, North American Regional Reanalysis = 0.30 K/decade; Table 1). Both climate model simulations show weaker positive trends over the United States, with the RF simulation showing a stronger trend (0.21 K/decade) than the GLCC simulation (0.16 K/decade) (Table 1). In addition, when analyzing only those grid points for which land cover is different between the modern and preindustrial datasets (Fig. 1b), the RF simulation shows more strongly positive trends than the GLCC simulation for areas changed to crop/mixed farming (0.12 and −0.01 K/decade, respectively), areas changed to irrigated crop (0.15 and 0.11 K/decade, respectively), and areas not designated as either crop type in the GLCC simulation (0.21 and 0.16 K/decade, respectively).
4.1 Mechanisms of climate response to land cover change
The dominant climate response to the modern non-urban land cover distribution is cooling of the continental United States, particularly during the warm-season. This statistically significant cooling is driven by changes in both surface moisture balance and surface albedo. For instance, in the Great Plains, where crops were exchanged for short grass, spring and summer display increased precipitation and soil moisture in the GLCC simulation (Figs. 3, 4). As a result of this enahanced surface moisture, these areas also display enhanced evapotranspiration, along with reduced sensible heat flux and cooler seasonal temperatures. This surface moisture effect is even stronger over the irrigated areas of the western United States that show statistically significant cooling (despite little change in warm-season precipitation), resulting in even larger cooling of surface air temperatures than in most other parts of the domain. The strength of this cooling in irrigated areas is likely exaggerated by the BATS treatment that sets the soil moisture to field capacity throughout the year. Conversely, in the areas of the Midwest that show statistically significant warm-season temperature changes, increases in vegetation albedo contribute to decreases in net surface shortwave flux, overcoming decreases in evapotranspiration to create seasonal decreases in sensible heat flux and associated net cooling (Figs. 3, 4). Finally, changes in both surface moisture balance and surface albedo play a role in the temperature response in the areas of statistically significant warm-season cooling in southern Texas. In these areas, conversion of interrupted forest to crop/mixed farming leads to increases in surface soil moisture and evapotranspiration (along with increases in precipitation) (Figs. 3, 4). The conversion to crops also leads to increases in vegetation albedo (Fig. 11) that contributes to decreases in net surface shortwave flux. Thus, both the surface moisture effect and the surface albedo effect contribute to decreased warm-season sensible heat flux and seasonal cooling over southern Texas.
A number of previous studies report that crops cool the surface relative to the corresponding potential vegetation (e.g., Bonan 1997, 1999; Bounoua et al. 2002; Feddema et al. 2005a; Govindasamy et al. 2001; Lobell et al. 2006a; Oleson et al. 2004). For instance, crop-induced cooling in the central United States is a common result in GCM sensitivity experiments (e.g., Betts et al. 2007; Bonan 1997, 1999; Feddema et al. 2005a; Govindasamy et al. 2001). This cooling has been attributed to changes in net radiation associated with surface albedo (Betts et al. 2007; Feddema et al. 2005a; Govindasamy et al. 2001) and/or moisture flux (Bonan 1997, 1999; Oleson et al. 2004). These modeling results for the central United States are supported by analyses of observational data, which suggest that the historical shift from forest to crops caused cooling of the Midwest United States (Bonan 2001). An exception in the literature is Ramankutty et al. (2006), who found that crops induce warm-season warming by decreasing latent heat flux.
The experiments reported here show considerably larger cooling over irrigated crop than non-irrigated crop grid points, with the simulated response of the surface moisture and energy budgets being stronger over irrigated crops. This basic radiative effect of irrigation has also been reported for a number of regions of the globe (e.g., Lobell et al. 2006a), and irrigation in the Central Valley of California has been shown to cause local cooling in a number of climate models (Kueppers et al. 2007, 2008). Further, observed expansion of irrigation has been linked to observed cooling of summer daytime temperatures (Bonfils and Lobell 2007).
4.2 Implications for observed temperature trends
The results presented here also give some indication that the presence of crop areas could have influenced the trend in surface air temperature over the late twentieth century period. Not only is the United States annual temperature trend more positive in the simulation without crops (RF) than in the simulation with crops (GLCC), but replacement of crop areas with potential vegetation reduces the slope of temperature change in those areas (Table 1). However, these trend differences are relatively small. Further, replacement of crop areas with potential vegetation has limited effect on the time evolution of annual temperature anomalies at those gridpoints (expressed as a difference from the respective long-term mean of each dataset) (Fig. 7). Based on these results, the influence of crop presence on recent United States surface air temperature is equivocal.
However, it should be noted that agricultural practices can influence surface climate (e.g., Lobell et al. 2006b), and changes in practice could therefore have influenced late twentieth century temperature trends independent of changes in crop distribution. Further, the experiments reported here did not include urban land cover. The trend in annual temperature for the United States domain is greater in the Climate Research Unit and Willmott–Matsuura datasets than in either the RF or GLCC simulation (Table 1). Both of those station-based datasets reflect the influence of expanded urban areas on surface temperature trends, indicating that the absence of urban areas in the climate model experiments could have damped the warming simulated over the 1988–2002 period.
4.3 Implications for future land cover changes
The results presented here suggest that future changes in land use could substantially affect climate by altering biophysical land–atmosphere interactions. Indeed, the changes in warm-season precipitation and evapotranspiration are similar in magnitude to those projected from high-resolution simulations of late-twenty-first century greenhouse gas forcing in the United States (e.g., Diffenbaugh et al. 2005), while the changes in warm-season temperature are similar in magnitude to those projected from high-resolution simulations of mid-twenty-first century greenhouse gas forcing (e.g., Pan et al. 2004). Land use change should therefore be considered along with greenhouse gas forcing when planning for—or attempting to avoid—potential long-term changes in local and regional climate.
Indeed, the effort to reduce greenhouse gas-induced climate change could itself affect local and regional climate. Mitigation efforts are creating economic pressures that could cause land cover change, both through incentives to sequester carbon on land, and through incentives to reduce fossil carbon emissions through combustion of biofuels. The experiments reported here suggest that if economic incentives cause forest plantations to replace traditional crops (as in the economic modeling of Jackson et al. 2005), those carbon sequestration efforts could result in local and regional warming at mid-latitudes, particularly during the warm-season. Conversely, should economic incentives cause crop-based biofuel production to replace forests, those land cover conversions could result in local and regional cooling at mid-latitudes. One major source of uncertainty is the extent to which regional irrigation would change along with those land cover conversions, especially given changes in plant water use efficiency at high atmospheric carbon dioxide concentrations (e.g., Diffenbaugh 2005a; Diffenbaugh et al. 2003).
Efforts to specifically quantify the effects of carbon sequestration on surface climate are mixed. On the one hand, several studies suggest that enhanced sequestration will cause local and regional warming in the extratropics by reducing surface albedo (e.g., Bala et al. 2006, 2007; Betts 2000; Betts et al. 2007; Diffenbaugh 2005a). On the other hand, Jackson et al. 2005 found that, in repeated simulations of the month of July, replacement of crops with forest plantations in the eastern United States increased evapotranspiration and decreased surface air temperature.
I have tested the sensitivity of regional and local climate to the modern non-urban land cover distribution of the continental United States. This high-resolution climate model experiment reveals that crop areas cause substantial cooling over large areas of the country. Areas of statistically significant cooling include areas of the Great Plains where crop/mixed farming has replaced short grass, areas of the Midwest and southern Texas where crop/mixed farming has replaced interrupted forest, and areas of the western United States containing irrigated crops. This statistically significant warm-season cooling is driven by changes in both surface moisture balance and surface albedo, with changes in surface moisture balance dominating in the Great Plains and western United States, changes in surface albedo dominating in the Midwest, and both effects contributing to warm-season cooling over southern Texas. In addition, the late twentieth century United States annual temperature trend is more positive in the simulation without crops than in the simulation with crops, but these trend differences are relatively small.
These results have important implications for future climate, energy, and land use policies. For instance, future conversion from crop to other land types could cause warming (particularly through urbanization (Kueppers et al. 2007)) and afforestation for carbon sequestration (e.g., Diffenbaugh 2005a; Jackson et al. 2008), while future expansion of crop area could cause cooling (particularly through expansion into marginal areas that require substantial irrigation). Further, in addition to direct influences on climate, the presence of agriculture could suppress regional and local warming at high greenhouse gas levels (Diffenbaugh et al. 2005; White et al. 2006), meaning that there could be secondary climatic effects of transitioning crops to forests as greenhouse gas concentrations continue to rise. The results presented here therefore suggest that the climatic effects of land cover change should be carefully considered when crafting policies for regulating land use and for managing anthropogenic forcing of the climate system.
I thank two anonymous reviewers for constructive and insightful insights. NCEP-DOE Reanalysis data provided by the NOAA-CIRES Climate Diagnostics Center, Boulder, Colorado, USA, from their website at http://www.cdc.noaa.gov/. This work was supported in part by NSF awards 0315677 and 0450221, and DOE award DE-FG02-08ER64649. The climate model simulations and analyses were carried out using computational resources in the Rosen Center for Advanced Computing (RCAC) at Purdue University, which is supported and administered by Information Technology at Purdue (ITaP). This is PCCRC paper number 0708.
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